Journal of Applied Science Studies - Ozean Publications
Journal of Applied Science Studies - Ozean Publications
Journal of Applied Science Studies - Ozean Publications
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Volume 3, Issue 1<br />
March 2010<br />
Spectra out <strong>of</strong> Oxygen and Ozone in Dielectric Barrier<br />
Discharge.<br />
M. A. HASSOUBA and N. DAWOOD<br />
Extension Mechanisms Influencing The Adoption Of Sprinkler<br />
Irrigation System In Iran<br />
SEYED JAMAL F.HOSSEINI, YOSRA KHORSAND and SHABALDEEN<br />
SHOKRI<br />
Geoelectric Assessment Of Groundwater Prospect And<br />
Vulnerability Of Overburden Aquifers At Idanre, Southwestern<br />
Nigeria<br />
OMOSUYI, G.O.<br />
Comparative vegetative and foliar epidermal features <strong>of</strong> three<br />
Paspalum L. species in Edostate, Nigeria.<br />
E.A OGIE-ODIA, A.I MOKWENYE, O. KEKERE and O. TIMOTHY<br />
Digital Moulding <strong>of</strong> the Solicitations within the Dielectric <strong>of</strong><br />
the Transformers and the Evaluation <strong>of</strong> Life Cycle <strong>of</strong> the<br />
Insulation Systems<br />
MARIUS-CONSTANTIN POPESCU and CRISTINEL POPESCU<br />
A disconnect congestion detection from TCP to improve the<br />
robustness<br />
ISSA KAMAR and SEIFEDDINE KADRY<br />
Analysis Of Microwave Signal Reception Using Finite<br />
Difference Implementation. (A Case Study Of Akure – Owo<br />
Digital Microwave Link In South Western Nigeria)<br />
OTASOWIE P.O and UBEKU E.U.<br />
Estimation <strong>of</strong> C factor for soil erosion modeling using NDVI in<br />
Buyukcekmece watershed<br />
AHMET KARABURUN<br />
<strong>Journal</strong> <strong>of</strong><br />
<strong>Applied</strong> <strong>Science</strong><br />
Physiological properties studies on essential oil <strong>of</strong> Jasminum<br />
grandiflorum L. as affected by some vitamins<br />
RAWIA.A.EID, LOBNA, S. TAHA and SOAD , M.M. IBRAHIM<br />
Effect <strong>of</strong> zinc and / or iron foliar application on growth and<br />
essential oil <strong>of</strong> sweet basil (Ocimum basilicum L.) under salt<br />
stress<br />
H.A.H. SAID-AL AHL and ABEER A. MAHMOUD<br />
Growth and yield <strong>of</strong> Foeniculum vulgare var.azoricum as<br />
influenced by some vitamins and amino acids<br />
S.F. HENDAWY and AZZA A.EZZ EL-DIN<br />
Effect <strong>of</strong> water stress and potassium humate on the<br />
productivity <strong>of</strong> oregano plant using saline and fresh water<br />
irrigation<br />
H.A.H. SAID-AL AHL and M.S. HUSSEIN<br />
Influence <strong>of</strong> Foliar Application <strong>of</strong> Pepton on Growth, Flowering<br />
and Chemical Composition <strong>of</strong> Helichrysum bracteatum Plants<br />
under Different Irrigation Intervals.<br />
SOAD , M.M. IBRAHIM, LOBNA, S. TAHA and M.M. FARAHAT<br />
Permeability and Porosity Prediction from Wireline logs Using<br />
Neuro-Fuzzy Technique<br />
WAFAA EL-SHAHAT AFIFY and ALAA H. IBRAHIM HASSAN<br />
Response <strong>of</strong> vegetative growth and chemical constituents <strong>of</strong><br />
Schefflera arboricola L. plant to foliar application <strong>of</strong> inorganic<br />
fertilizer (grow-more) and ammonium nitrate at Nubaria.<br />
MONA, H. MAHGOUB, EL-QUESNI, FATMA E.M. and MAGDA,M.<br />
KANDIL<br />
Statistical Modelling For Outlier Factors<br />
Ahmet KAYA
OZEAN JOURNAL <strong>of</strong><br />
APPLIED SCIENCE<br />
A PEER REVIEVED INTERNATIONAL JOURNAL<br />
----------------------------------------------------------------------------------------------------------------------------------------------<br />
Volume 3, Issue 1, March 2010<br />
ONLINE ISSN 1943-2542 PRINTED ISSN: 1943-2429<br />
----------------------------------------------------------------------------------------------------------------------------------------------<br />
Gerald S. Greenberg, Ohio State University, USA<br />
Hakki Yazici, Afyon Kocatepe University, Turkey<br />
Hayati Akyol, Gazi University, Turkey<br />
Hayati Doganay, Ataturk University, Turkey<br />
Laurie Katz, Ohio State University, USA<br />
Lisandra Pedraza, University <strong>of</strong> Puerto Rico in<br />
Rio Piedras, Puerto Rico<br />
Lutfi Ozav, Usak University, Turkey<br />
Managing Editor<br />
Ali Ozel, Dumlupinar University<br />
Publication Coordinator<br />
Taskin Inan, Dumlupinar University<br />
Editorial Board<br />
Mihai Maxim, Bucharest University, Romania<br />
Ibrahim Atalay, Dokuz Eylul University, Turkey<br />
Ibrahim S. Rahim, National Research Center, Egypt<br />
Janet Rivera, NOVA University, USA<br />
Ramazan Ozey, Marmara University, Turkey<br />
Samara Madrid, Northern Illinois University, USA<br />
Samia Abdel Aziz-Ahmed Sayed, National Research<br />
Center, Egypt<br />
Web: http://www.ozelacademy.com E-mail: editorejes@gmail.com<br />
Copyright © 2008 <strong>Ozean</strong> Publication, 2141 Baneberry Ct. 43235, Columbus, Ohio, USA
<strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
OZEAN JOURNAL <strong>of</strong><br />
APPLIED SCIENCE<br />
A PEER REVIEVED INTERNATIONAL JOURNAL<br />
---------------------------------------------------------------------------------------------------------------------------------<br />
Volume 3, Issue 1, March 2010<br />
ONLINE ISSN 1943-2542 PRINTED ISSN: 1943-2429<br />
---------------------------------------------------------------------------------------------------------------------------------<br />
Spectra out <strong>of</strong> Oxygen and Ozone in Dielectric Barrier Discharge.<br />
M. A. HASSOUBA and N. DAWOOD<br />
Extension Mechanisms Influencing The Adoption Of Sprinkler Irrigation System In Iran<br />
SEYED JAMAL F.HOSSEINI, YOSRA KHORSAND and SHABALDEEN SHOKRI<br />
Geoelectric Assessment Of Groundwater Prospect And Vulnerability Of Overburden Aquifers At<br />
Idanre, Southwestern Nigeria<br />
OMOSUYI, G.O.<br />
Comparative vegetative and foliar epidermal features <strong>of</strong> three Paspalum L. species in Edostate,<br />
Nigeria.<br />
E.A OGIE-ODIA, A.I MOKWENYE, O. KEKERE and O. TIMOTHY<br />
Digital Moulding <strong>of</strong> the Solicitations within the Dielectric <strong>of</strong> the Transformers and the Evaluation <strong>of</strong><br />
Life Cycle <strong>of</strong> the Insulation Systems<br />
MARIUS-CONSTANTIN POPESCU and CRISTINEL POPESCU<br />
A disconnect congestion detection from TCP to improve the robustness<br />
ISSA KAMAR and SEIFEDDINE KADRY<br />
Analysis Of Microwave Signal Reception Using Finite Difference Implementation. (A Case Study Of<br />
Akure – Owo Digital Microwave Link In South Western Nigeria)<br />
OTASOWIE P.O and UBEKU E.U.<br />
Estimation <strong>of</strong> C factor for soil erosion modeling using NDVI in Buyukcekmece watershed<br />
AHMET KARABURUN<br />
Physiological properties studies on essential oil <strong>of</strong> Jasminum grandiflorum L. as affected by some<br />
vitamins<br />
RAWIA.A.EID, LOBNA, S. TAHA and SOAD , M.M. IBRAHIM<br />
Effect <strong>of</strong> zinc and / or iron foliar application on growth and essential oil <strong>of</strong> sweet basil (Ocimum<br />
basilicum L.) under salt stress<br />
H.A.H. SAID-AL AHL and ABEER A. MAHMOUD<br />
Growth and yield <strong>of</strong> Foeniculum vulgare var.azoricum as influenced by some vitamins and amino<br />
acids<br />
S.F. HENDAWY and AZZA A.EZZ EL-DIN
<strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Effect <strong>of</strong> water stress and potassium humate on the productivity <strong>of</strong> oregano plant using saline and<br />
fresh water irrigation<br />
H.A.H. SAID-AL AHL and M.S. HUSSEIN<br />
Influence <strong>of</strong> Foliar Application <strong>of</strong> Pepton on Growth, Flowering and Chemical Composition <strong>of</strong><br />
Helichrysum bracteatum Plants under Different Irrigation Intervals.<br />
SOAD , M.M. IBRAHIM, LOBNA, S. TAHA and M.M. FARAHAT<br />
Permeability and Porosity Prediction from Wireline logs Using Neuro-Fuzzy Technique<br />
WAFAA EL-SHAHAT AFIFY and ALAA H. IBRAHIM HASSAN<br />
Response <strong>of</strong> vegetative growth and chemical constituents <strong>of</strong> Schefflera arboricola L. plant to foliar<br />
application <strong>of</strong> inorganic fertilizer (grow-more) and ammonium nitrate at Nubaria.<br />
MONA, H. MAHGOUB, EL-QUESNI, FATMA E.M. and MAGDA,M. KANDIL<br />
Statistical Modelling For Outlier Factors<br />
Ahmet Kaya<br />
Web: http://www.ozelacademy.com E-mail: editorejes@gmail.com<br />
Copyright © 2008 <strong>Ozean</strong> Publication, 2141 Baneberry Ct. 43235, Columbus, Ohio, USA<br />
A peer revieved international journal<br />
ONLINE ISSN 1943-2542 PRINTED ISSN: 1943-2429<br />
http://ozelacademy.com/ojas.htm
<strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Spectra out <strong>of</strong> Oxygen and Ozone<br />
in Dielectric Barrier Discharge.<br />
M. A. Hassouba* and N. Dawood<br />
<strong>Applied</strong> Physics Dept., Faculty <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s, Taibah Univ., KSA.<br />
*E-mail address for correspondence: hassouba@yahoo.com<br />
________________________________________________________________________________________<br />
Abstract: Dielectric-barrier discharges (DBD) are very attractive for industrial applications because they can<br />
provide nonequilibrium plasma conditions at about atmospheric pressure. DBD is an excellent source <strong>of</strong> ideal<br />
energetic electrons with 1–10 eV and high density. Its unique advantageous is to generate low excited atomic<br />
and molecular species, free radicals and excimers with several electron volt energy.Spectra out <strong>of</strong> ozone<br />
synthesis system, in dielectric barrier discharge (DBD) using oxygen gas, have been detected in the range <strong>of</strong> 300<br />
to 400 nm. The dependence <strong>of</strong> spectral intensity on the discharge voltage and the oxygen pressure has been<br />
studied. The half-width <strong>of</strong> the detected lines was found to be within 20 A o approximately. Spectroscopic<br />
technique is a well-known technique for the measurement <strong>of</strong> the mean electron temperature in the gas discharge.<br />
The electron temperature within the microdischarge has been estimated by using the relative intensity <strong>of</strong> the line<br />
to line ratio technique <strong>of</strong> the identified spectral lines. An average mean electron temperature <strong>of</strong> 3.6 eV was<br />
obtained and it has been found to be insensitive to the gas pressure variation.<br />
Key Words:- Dielectric Barrier Discharge, Ozone Spectra, Electron Temperature<br />
measurements ,Plasma Spectroscopic Models.<br />
__________________________________________________________________________________________<br />
INTRODUCTION<br />
Dielectric-barrier discharges (silent discharges) combine the ease <strong>of</strong> atmospheric pressure operation with<br />
nonequilibrium plasma conditions suited for many plasma chemical processes. In most gases at this pressure the<br />
discharge consists <strong>of</strong> a large number <strong>of</strong> randomly distributed short-lived microdischarges.. Traditionally mainly<br />
used for industrial ozone production, dielectric-barrier discharges have found additional large volume<br />
applications in surface treatment, high-power CO2 lasers, excimer ultraviolet lamps, pollution control and, most<br />
recently, also in large-area flat plasma display panels. Future applications may include their use in greenhouse<br />
gas control technologies [1].<br />
Many articles [1-7] have been published about the optical emission from DBDs by using other gases such as Xe,<br />
Cl, Ar, He. The dielectric barrier discharges (silent discharge) <strong>of</strong>fer the possibility <strong>of</strong> building large area and<br />
high intensity UV-sources, for industrial processing.<br />
Burm [8] investigate two plasma sources, an air plasma torch and a nitrogen dielectric barrier discharge. Optical<br />
emission spectroscopy is used to determine the heavy particles and the vibration (electron) temperatures for the<br />
two plasma sources. The two temperatures are measured to obtain an estimation <strong>of</strong> the deviation from local<br />
thermal equilibrium and to compare the two source configurations which are used for surface treatment.<br />
The present work is originally directed toward the design <strong>of</strong> a cheap and simple DBD ozonizer [9]. The spectra<br />
out from this system have been detected and the electron temperature <strong>of</strong> the discharge is determined using the<br />
spectroscopic method.<br />
1
The experiment setup consists <strong>of</strong> two parts<br />
1- Discharge Cell<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
EXPERIMENTAL SETUP<br />
In the present work, the cell <strong>of</strong> the discharge consists <strong>of</strong> coaxial electrodes. The inner electrode has been made <strong>of</strong><br />
brass rod with radii 0.5 cm. The outer electrode is made <strong>of</strong> graphite coated on the outer wall <strong>of</strong> a Silica glass<br />
tube, which has been used as a dielectric material and as a window for the study output radiation <strong>of</strong> the system.<br />
The gap space between the inner electrode and the inner wall <strong>of</strong> glass tube was 0.175 cm. The length <strong>of</strong> the<br />
reactor region was 30 cm and the pressure <strong>of</strong> gas could be controlled by the needle valves, which enable<br />
controlling the flow rate in the system. The pressure inside the discharge tube was measured by using manometer<br />
and gauge model P200-H (RS-497-606) which enables the pressure to be measured in the range from 1 to 2.25<br />
bars within 1 mbar experimental error. The flow rate <strong>of</strong> oxygen (98.7% purity) has been measured by using a<br />
flow meter (Cole Parmer). Figure (1) shows the present DBD system.<br />
The electric circuit <strong>of</strong> the discharge is also shown in Fig. (1) which consists <strong>of</strong> AC power supply (0�220 V , 50<br />
Hz) connected to a high voltage transformer with a variable output, 0�20 kV. In order to measure the applied<br />
potential across the discharge cell, a potential divider has been built, which consists <strong>of</strong> two resistors in the ratio<br />
<strong>of</strong> (1/450) connected in parallel with the discharge cell. Only the potential difference across the lower part <strong>of</strong> the<br />
divider is measured, and then the actual applied potential across the cell can be estimated.<br />
2- The Spectroscopic Setup<br />
Figure (2) shows the present spectroscopic setup, which is controlled by PC computer. The spectroscopic<br />
devices <strong>of</strong> type Oriel, consists <strong>of</strong> mono-chromator 25 cm path length and has a diffraction grating <strong>of</strong> 1200<br />
mm. The relative intensity <strong>of</strong> lines has been measured by using photo-multiplier (PMT) capable <strong>of</strong> measuring the<br />
spectra in the range <strong>of</strong> 185–650 nm. PMT connect to readout system for reading the intensity <strong>of</strong> light, the readout<br />
capable <strong>of</strong> current amplification up to 10 9 A. PC computer with interface and stepper motor driver has been used<br />
to control in the motion <strong>of</strong> the grating, so that it enables to variation <strong>of</strong> the wavelength one angstrom by step.<br />
1- Spectra <strong>of</strong> Oxygen in Silent Discharge<br />
RESULTS AND DISCUSSION<br />
The only detectable spectra have been found in the region from 300 to 400 nm. The absorption cross section <strong>of</strong><br />
ozone is known to be high in two ranges; Hartly band; 160 - 320 nm and Chappuis band; 420-730 nm [10].<br />
Therefore, no spectra emission could be seen or measured in these two ranges.<br />
Typical spectrums <strong>of</strong> DBD at different pressure and discharge voltages are shown in Figs. (3-a, b and c).<br />
It is noticed that, the emitted lines could not be detected until the applied potential reached the onset potential<br />
where the ozone starts to build up, which depends on the working gas pressure p, inner electrode distance d and<br />
the type <strong>of</strong> the dielectric material and its thickness T.<br />
e= e/d =<br />
constant * V/p), where q is the electron charge, V is the applied voltage, d is the gap space distance between the<br />
e is the mean free path <strong>of</strong> the electrons.<br />
Figure (4) shows a typical graph for the present relation between (VB) and (p*d) in oxygen (right hand side <strong>of</strong> the<br />
Paschen Curve) under the given conditions where VB is increasing linearly with (p*d). Also as a ozone<br />
composition is a chemical reaction it is therefore the current is the main parameter which controls the number <strong>of</strong><br />
ozone reactions that take place in this system. Figure (5) shows the relation between the voltage and the current<br />
flowing in the system at different gas pressures.<br />
2
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
When the pressure is kept constant the mean free path is constant but if the applied voltage is increased, the<br />
number <strong>of</strong> electrons capable on excitation and ionization increases. Therefore, it is expected in this case that the<br />
intensity <strong>of</strong> the emitted lines will increase with the applied potential, [at p=1.25 bar]. Also, when the pressure<br />
increases the collision frequency increases, therefore the intensity <strong>of</strong> the emitted lines increases.<br />
It can be noticed that the half width <strong>of</strong> any <strong>of</strong> these lines is less than 2 nm, which could be, used more or less as a<br />
monochromatic radiation [10]. Such radiation could be easily generated on a large scale for the purpose <strong>of</strong><br />
industrial applications [11].<br />
2- Mean Electron Temperature.<br />
Spectroscopic technique is a well-known technique for the measurement <strong>of</strong> the mean electron temperature in the<br />
gas discharge.<br />
In the present work not all the radiation lines has been identified, although pure oxygen <strong>of</strong> 98.7% purity has<br />
been used and unfortunately only few lines <strong>of</strong> them has been identified and were therefore used for the deriving<br />
<strong>of</strong> the electron temperature.<br />
The line to line relative intensity ratio technique (for the same ionization stage) is used to determine the<br />
mean electron temperature, Te, in silent discharge, according to the following equation [11]:-<br />
Where: -<br />
K is the Boltzmann`s constant, Te is the mean electron temperature, I, I’ are the relative intensity <strong>of</strong> the two<br />
given lines, �, � ` are the wavelengths <strong>of</strong> two lines, g, g ` are the statistical weight <strong>of</strong> two lines, f, f ` are the<br />
oscillator strength <strong>of</strong> two lines, E` is the excitation energy for the higher ionization stage and E is the excitation<br />
energy for the lower ionization stage. The lines identified are <strong>of</strong> the wavelengths tabulated in Table (1), together<br />
with their values <strong>of</strong> the above parameters [11]. The intensities <strong>of</strong> the identified lines were taken from the<br />
measured discharge spectra in Fig. (3).<br />
Wavelength (�)<br />
A o<br />
'<br />
(E � E)<br />
KTe<br />
�<br />
3 ' '<br />
I�<br />
g f<br />
ln( )<br />
' 3<br />
I � gf<br />
Table (1) The parameters <strong>of</strong> the selected lines used in the calculation.<br />
Excitation<br />
Energy (E)<br />
Oscillator<br />
Strength (f)<br />
3<br />
Statistical<br />
Weight (g)<br />
Product <strong>of</strong><br />
(f) x (g)<br />
3709.5 45.07 eV 0.0747 1 0.0747<br />
3754.7 36.29 eV 0.277 5 1.385<br />
3911.96 28.71 eV 0.0326 4 0.130<br />
3945 26.45 eV 0.113 4 0.452<br />
In order to derive the mean electron temperature from the above equation two couples <strong>of</strong> lines have to be chosen<br />
so that their wavelengths are very near to each other, and from the same stage <strong>of</strong> ionization.<br />
The parameters <strong>of</strong> these couples <strong>of</strong> lines were substituted in the equation and hence the mean electron<br />
temperature was calculated and has been tabulated below.<br />
The results for the couple <strong>of</strong> lines <strong>of</strong> wavelengths 391.19 nm and 394.5 nm emitted from O + are shown in Table<br />
(2). Also, the results <strong>of</strong> the couple <strong>of</strong> lines <strong>of</strong> wavelengths 370.95 nm and 375.47 nm, which emitted from O ++<br />
are shown in Table (2).
Pressure<br />
(bar)<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table (2) Shows the results for the couple <strong>of</strong> lines <strong>of</strong> wavelengths 391.19 nm<br />
and 394.5 nm emitted from O + at different conditions.<br />
Lines 391.19 nm and 394.5 nm Lines 370.9 nm and 375.47 nm<br />
V (dis.)<br />
18 kV<br />
Electron<br />
Temp.(Te)<br />
V(dis.)<br />
13.5 kV<br />
Electron<br />
Temp.(Te)<br />
4<br />
V (dis.)<br />
18 kV<br />
Electron<br />
Temp. (Te)<br />
V(dis.)<br />
13.5 kV<br />
Electron<br />
Temp. (Te)<br />
1.005 3.77 eV 3.6 eV 3.8 eV 3.4 eV<br />
1.25 3.6 eV 3.7 eV 3.6 eV 3.2 eV<br />
1.5 3.7 eV 3.7 eV 3.8 eV 3.4 eV<br />
1.75 3.77 eV 3.8 eV 3.85 eV 3.4 eV<br />
The mean electron temperature has been drawn as a function <strong>of</strong> gas pressure and applied voltage and is shown in<br />
Fig. (6-a, b).<br />
It can be noticed from Fig. (6-a, b) that the mean electron temperature in the dielectric barrier discharge is nearly<br />
constant at a mean electron temperature is 3.6 eV and does not depend on the gas pressure.<br />
CONCLUSION<br />
The silent discharge is a non-equilibrium discharge which can be operated up to pressures <strong>of</strong> several bars. It is<br />
industrially used on a large scale for the generation <strong>of</strong> ozone from air or oxygen. Ozone generators have a typical<br />
power consumption ranging from some kilowatts to several megawatts. The main characteristic <strong>of</strong> the silent<br />
discharge is that narrow discharge gaps <strong>of</strong> a few millimeter spacing are used and that at least one <strong>of</strong> the<br />
electrodes is covered by an insulating layer. For this reason the silent discharge is also referred to as the<br />
"dielectric-barrier discharge" (DBD).<br />
The present work is originally directed toward the design <strong>of</strong> a cheap and simple DBD ozonizer.<br />
It is noticed that, the emitted lines could not be detected until the applied potential reached the onset potential<br />
where the ozone starts to build up, which depends on the working gas pressure p, inner electrode distance d and<br />
the type <strong>of</strong> the dielectric material and its thickness T<br />
Spectroscopic technique is a well-known technique for the measurement <strong>of</strong> the mean electron temperature in the<br />
gas discharge.<br />
It is concluded that, that the mean electron temperature in the dielectric barrier discharge is nearly constant at a<br />
mean electron temperature is 3.6 eV and does not depend on the gas pressure.
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
FIGURES<br />
Figure (1) shows the discharge Cell.<br />
PC Computer Steeper Motor<br />
P.S. for PMT<br />
A/D Converter Readout Amp.<br />
Figure (2) shows the spectroscopic setup.<br />
5<br />
PMT<br />
Mono- Plasma<br />
chromator Source
Intensity (Arb. Unit)<br />
Silica<br />
p=1.25 bar<br />
V(dis.)=13.5 KV<br />
300 320 340 360 380 400<br />
Wavelength (nm)<br />
Intensity (Arb. Unit)<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
3<br />
2<br />
2<br />
1<br />
1<br />
CB<br />
BA<br />
0<br />
300 320 340 360 380<br />
Wavelength (nm)<br />
400<br />
6<br />
B<br />
Silica<br />
p.=1.75 bar<br />
V(dis)=18 kV<br />
Figure (3-A, B and C) show the spectra <strong>of</strong> the discharge at different conditions and at T =0.15 cm, d<br />
= 0.175 cm and L = 30 cm.
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Figure (4) shows the relation between V (breakdown) and (pressure*gap space).<br />
Figure (5) shows the relation between I(dis.) and V(dis.) at d=0.175 cm, L=30 cm and<br />
T=0.15 cm<br />
7
Ele.Temp.(eV)<br />
Ele.Temp.(eV)<br />
5<br />
4<br />
3<br />
2<br />
1<br />
0<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
O(++)<br />
3709.5 A<br />
& 3754.7 A<br />
0.75 1.00 1.25 1.50 1.75 2.00<br />
Pressure (bar)<br />
5<br />
4<br />
3<br />
2<br />
1 O(+)<br />
3911.96<br />
0<br />
& 3954.7 A<br />
0.75 1.00 1.25 1.50 1.75 2.00<br />
Pressure (bar)<br />
Figure-(6-A, B) show the Figure relation between (7-a, the b) electron show the temperature relation and between the pressure the at + electron 13.5 and temperature 18.0 KV an<br />
at 13.5 and 18.0 KV<br />
8<br />
BA<br />
AB
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
REFERENCES<br />
A.A.Garamoon, F.F.Elakshar and A.M.Nossair, (1999), GEC 52 nd , Virginia, USA, 324.<br />
A.Baulch, (1980), J. Phys. Chem. Ref. Data, 9, 296.<br />
H.R.Griem, (1964), Plasma Spectroscopy , McGraw-Hill, New York., p.382..<br />
Haile Lei, Yongjian Tang, Jun Li, and Jiangshan Luo, (2007), Appl. Phys. Lett. 91, 113119.<br />
K.G. Kostov; R. Y. Honda; L.M.S. Alves and M.E. Kayama Braz, (2009), J. Phys., 39, 2.<br />
K.T.A. Burm, (2005), Contrib. Plasma Phys., 45, 54.<br />
M.P.Milden, (2001), J. <strong>of</strong> Phys. D: Appl. Phys. 34, L1.<br />
Takaaki Tomai, Tsuyohito Ito and Kazuo Terashima, (2006), Thin Solid Films, 507 , 409.<br />
U.Kogelschatz, (1997), J. de Physique IV, 7, C4-47 to C4-66.<br />
U.Kogelschatz, (1997), ICPIG XXIII, Toulouse, France, 1.<br />
Ulrich Kogelschatz², Baldur Eliasson and Walter Egli, (1999), Pure Appl. Chem., 71, 1819.<br />
Young Sun Mok, (2005), XXVIIth ICPIG, Eindhoven, the Netherlands, 18-22 July, PP. 18.<br />
9
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Extension mechanisms influencing the adoption <strong>of</strong> sprinkler irrigation system in Iran<br />
Seyed Jamal F.Hosseini*, Yosra Khorsand** and Shabaldeen Shokri***<br />
*Islamic Azad University, <strong>Science</strong> and Research Branch Tehran, Iran<br />
**Islamic Azad University, Birjand branch Birjand, Iran<br />
***Department <strong>of</strong> Agricultural development Islamic Azad University, <strong>Science</strong> and Research Branch<br />
Tehran, Iran<br />
*Email address for correspondence: jamalfhosseini@yahoo.com<br />
__________________________________________________________________________________________<br />
Abstract: Horticultural producers were surveyed in order to explore their perception about the role <strong>of</strong> extension<br />
mechanisms in adopting the sprinkler irrigation system in Iran. The methodology used in this study involved a<br />
combination <strong>of</strong> descriptive and quantitative research. The total population for this study was 150 gardeners who<br />
adopted the sprinkler irrigation system in Chenaran Township in Khorasan Razavi Province. Based on the<br />
results <strong>of</strong> the mean score, respondents indicated that visiting extension agents in the service centers was the<br />
most effective individual extension method main in helping them to adopt the sprinkler irrigation systems. It was<br />
also reported from the findings <strong>of</strong> the study 45% <strong>of</strong> the variance in the perception <strong>of</strong> gardeners about the role <strong>of</strong><br />
extension mechanisms in adopting the sprinkler irrigation systems could be explained by visiting extension<br />
agents in service centers, extension classes, visiting extension agents in the field and visiting sample farm.<br />
Kewords: Extension Mechanisms, Sprinkler Irrigation System, Iran, Gardener.<br />
__________________________________________________________________________________________<br />
INTRODUCTION<br />
World Bank predicted that by the year 2035, three billion people will live in the tough conditions because <strong>of</strong><br />
water shortage (World Bank, 2009). According to the Human Development Report, by the year 2080 climate<br />
change would affect the life <strong>of</strong> many people throughout the world and more than 1.8 billion people would face<br />
water shortages (UNDP, 2007, p.30).<br />
Today, there are several major issues in connection with the water sector in developing and developed countries<br />
which include: water cycle, quality <strong>of</strong> life, equality <strong>of</strong> water, sustainability and human rights (Sohail and Cavill,<br />
2006). In Iran, the policy <strong>of</strong> government has been to increase agricultural production for various reasons, such as<br />
price stability, improved per capita income and increased need for non-oil foreign exchange resources and this<br />
trend has become an unavoidable reality for agricultural sector. Increasing agricultural production has resulted<br />
in consumption <strong>of</strong> more water and there is no other way to change the amount <strong>of</strong> water used which is the<br />
equivalent <strong>of</strong> 130 billion cubic meters a year unless to use water more efficiently and to adopt new methods <strong>of</strong><br />
irrigation.<br />
Consumption <strong>of</strong> water by agriculture sector in Iran has always been an issue <strong>of</strong> concerns which caused by high<br />
water losses in farm fields, farms inappropriate shape and size, lack <strong>of</strong> knowledge <strong>of</strong> farmers about making<br />
optimum use <strong>of</strong> water, rapid destruction <strong>of</strong> water infrastructure, loss in quality <strong>of</strong> irrigation networks,<br />
inappropriate methods <strong>of</strong> irrigation, irrigation efficiency and loss <strong>of</strong> water in irrigation systems (Keshavarz,<br />
2000).<br />
Omani et al (2009) citing Keshavarz, Heydari, and Ashrafi (2003) pointed out that the overall irrigation<br />
efficiency in Iran ranges from 33 to 37%, which is lower than the average for both developing countries (45%)<br />
and developed countries (60%).<br />
11
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Unfortunately, inefficient use <strong>of</strong> water in the past decades has nearly reduced more than 40 meter in<br />
underground water level (Unit, 2005). Currently, the total water consumption is approximately 88.5 bm3, out <strong>of</strong><br />
which more than 93% is used in agriculture, while less than 7% is allocated to urban and industrial<br />
consumption. Under the present situation 82.5 bm3 <strong>of</strong> water is utilized for irrigation on 7.5 million hectares <strong>of</strong><br />
land under irrigated agriculture (Ommani & Noorivandi, 2003).<br />
In order to combat this problem, there is need for new technologies and methods to manage water more<br />
efficiently especially in agricultural sector (Karami, Rezaei-Moghaddam, and Ebrahimi., 2006). On one hand a<br />
more comprehensive water management is needed to achieve sustainable development and participatory<br />
mechanism could accelerate this process (Guterstan, 2008). On the other hand the principle <strong>of</strong> sustainable<br />
development is an essential imperative for the water industry which should be seen as an opportunity not a<br />
limitation (Asheley et al. 2003).<br />
Khorasan Razavi province is among regions in Iran with low rainfall. The amount <strong>of</strong> evaporation and<br />
transpiration <strong>of</strong> rainfall in this province is very significant which is 2 to 3 times higher than the average in<br />
country. According to the latest statistics, total volume <strong>of</strong> water consumption from surface water and<br />
groundwater is 9261.8 million cubic meters and more than 8445 million cubic meters <strong>of</strong> this amount used in<br />
agricultural sector.<br />
The traditional methods <strong>of</strong> water management have many problems and the best option currently to use for<br />
irrigating farms is sprinkler irrigation systems. The results <strong>of</strong> Study show that implementation <strong>of</strong> this irrigation<br />
method resulted in decreasing rate <strong>of</strong> water consumption from 12,000 cubic meters in hectare to 6,200 cubic<br />
meters (Vojdani, 2006). Despite, financial facilities which are allocated each year for farmers, the participation<br />
<strong>of</strong> farmers has not reached to a satisfactory level.<br />
Agricultural extension by its nature has an important role in promoting the adoption <strong>of</strong> new technologies and<br />
innovations. Extension organizations have a key role in brokering between providers <strong>of</strong> technologies and<br />
farmers. However, adopting is rarely instantaneous; the technology has to be taught and learned, adapted to<br />
experience, and integrated into production. As is <strong>of</strong>ten the case with technological innovation, potential and<br />
expectations can outpace reality (Bonati and Gelb, 2005).<br />
Omani et al (2009) citing Evenson (1997) pointed out to this fact that agricultural extension and education as<br />
achieving its highest economic impact and sustainability in agriculture by providing information to increase<br />
farmers awareness, knowledge, adoption and productivity.<br />
Therefore, understanding the extension mechanisms which would speed up the development and adoption <strong>of</strong> the<br />
sprinkler irrigation system in the township <strong>of</strong> Chenaran in Khorasan Razavi Province was investigated in this<br />
research.<br />
MATERIAL AND METHODS<br />
The methodology used in this study involved a combination <strong>of</strong> descriptive and quantitative research and<br />
included the use <strong>of</strong> correlation, regression and descriptive analysis as data processing methods. The total<br />
population for this study was 150 gardeners who adopted the sprinkler irrigation system. Data were collected by<br />
using questionnaire and through interview schedules.<br />
A series <strong>of</strong> in-depth interviews were conducted with some senior experts in the Department <strong>of</strong> Agriculture and<br />
Power in the Khorasan Razavi Province to develop the questionnaire. The questionnaire included both openended<br />
and fixed-choice questions. The open-ended questions were used to gather information not covered by the<br />
fixed-choice questions and to encourage participants to provide feedback.<br />
Content and face validity were established by a panel <strong>of</strong> experts consisting <strong>of</strong> faculty members at Islamic Azad<br />
University, <strong>Science</strong> and Research Branch and some experts in the Departments <strong>of</strong> Agriculture and Power. A<br />
pilot study was conducted with 25 specialists who had not been interviewed before the earlier exercise <strong>of</strong><br />
determining the reliability <strong>of</strong> the questionnaire for the study. Computed Cronbach’s Alpha score was 85.0%,<br />
which indicated reliability <strong>of</strong> the questionnaire.<br />
Independent variables in the study included extension mechanisms and personal characteristics <strong>of</strong> respondents.<br />
The dependent variable in this research study were the adoption <strong>of</strong> the sprinkler irrigation system by gardeners...<br />
For measurement <strong>of</strong> correlation between the independent variables and the dependent variable correlation<br />
coefficients have been utilized and include spearman test <strong>of</strong> independence.<br />
12
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
RESULTS<br />
Table 1 summarizes the demographic pr<strong>of</strong>ile and descriptive statistics <strong>of</strong> respondents. The results <strong>of</strong> descriptive<br />
statistics indicated that average age <strong>of</strong> respondents was 46 years old and majority <strong>of</strong> respondents did not have<br />
high school diploma. The study shows that average work experience was 19 years and the main occupation <strong>of</strong><br />
respondents was farming and gardening. Approximately 43 percent <strong>of</strong> respondents owned their lands and the<br />
remainder either had a collective ownership or rented the land.<br />
Respondents were asked to respond the question about role <strong>of</strong> water shortages in implementing sprinkler<br />
irrigation system. As a result, 71 percent <strong>of</strong> respondents indicated that agricultural water shortage was the main<br />
factor in the implementation <strong>of</strong> the irrigation system.<br />
The perception <strong>of</strong> respondents about the sources which help them to acquire information about sprinkler<br />
irrigation systems was displayed in Table 2. The highest mean refers to extension agents (mean=3.58) and the<br />
lowest mean refers to experiment stations (mean=1.59).<br />
The results <strong>of</strong> perception <strong>of</strong> respondents about the role <strong>of</strong> communication channels which would influence the<br />
adoption <strong>of</strong> sprinkler irrigation systems by gardeners were displayed in Table 2. The results indicated that the<br />
highest mean number refers to extension agents (mean=4.11) and the lowest mean number refers to relatives<br />
(mean=1.67).<br />
The respondents’ perception about the role <strong>of</strong> extension mechanisms in adopting the sprinkler irrigation systems<br />
was displayed in Table 4. As can be seen from this table, the highest mean refers to visit by extension agents in<br />
agricultural service centers (mean=3.18) and the lowest mean refers to extension workshops (mean=2.57).<br />
Spearman coefficient was employed for measurement <strong>of</strong> relationships between perceptions <strong>of</strong> gardeners about<br />
the role <strong>of</strong> extension mechanisms in adopting the sprinkler irrigation system as dependent variable. Table 5<br />
displays the results which show that there was relationship between perception <strong>of</strong> respondents about the age,<br />
visiting extension agents in the service centers, extension classes, visiting the sample farm and visiting extension<br />
agents in the field and adopting the sprinkler irrigation system.<br />
Table 6 shows the result for regression analysis by stepwise method. Independent variables that were<br />
significantly related to perception <strong>of</strong> respondents about role <strong>of</strong> extension mechanisms in adopting the sprinkler<br />
irrigation system were entered. The result indicates that 45% <strong>of</strong> the variance in the perception <strong>of</strong> gardeners<br />
about the role <strong>of</strong> extension mechanisms in adopting the sprinkler irrigation systems could be explained by<br />
visiting extension agents in service centers, extension classes, visiting extension agents in the field and visiting<br />
sample farm.<br />
CONCLUSION<br />
The perception <strong>of</strong> gardeners about the role <strong>of</strong> extension mechanisms in adopting sprinkler irrigation system was<br />
discussed in this article. As the regression analysis showed visiting sample farms, visiting extension agents in<br />
the service centers and field and extension classes caused 45% <strong>of</strong> variance on the perception <strong>of</strong> respondents<br />
regarding the role <strong>of</strong> extension mechanisms in adopting sprinkler irrigation systems. This result is consistent<br />
with Okunade (2007) conclusion in which skill is better acquired through group contact methods. These<br />
methods have the nature <strong>of</strong> practical demonstration which will help the clientele from desire stage through<br />
conviction and probably into taking action. The individual contact method is considered to be important tool to<br />
help farmers to adopt a new technology. This may be as a result <strong>of</strong> the nature <strong>of</strong> the methods <strong>of</strong> giving<br />
information and deeper understanding <strong>of</strong> the innovation concerned.<br />
Based on the results <strong>of</strong> the study by Chizari, etal. (1998) the majority <strong>of</strong> extension agents believed the result<br />
demonstration were the most effective method for teaching their clientele. Result demonstrations are the<br />
processes <strong>of</strong> showing farmers the impact <strong>of</strong> using a particular practice. The second most effective method<br />
identified by extension agents was method demonstration. Method demonstrations typically occur after result<br />
demonstrations.<br />
Based on the results <strong>of</strong> the mean score, respondents indicated that visiting extension agents in the service centers<br />
was the most effective individual extension method main in helping them to adopt the sprinkler irrigation<br />
systems. The results demonstrated that respondents preferred individual teaching methods compared with group<br />
13
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
and mass methods. Although all agents use a variety <strong>of</strong> teaching methods, agricultural agents generally tend to<br />
use more individual methods than the other agents. Farm visits and on-farm demonstrations model the early<br />
farm demonstration method <strong>of</strong> providing research-based recommendations to the local producer.<br />
IMPLICATIONS<br />
The perception <strong>of</strong> gardeners about the extension mechanisms in adopting the sprinkler irrigation system was<br />
discussed in this article. The results demonstrated that visiting sample farms and face to face meetings with<br />
extension agents in service center and farms are the most important mechanisms in helping gardeners in<br />
adopting sprinkler irrigation systems. Successful adoption <strong>of</strong> this technology in Iran will depend on the<br />
appropriate government support and the authorities should develop policies that would overcome the challenges<br />
in adopting this method <strong>of</strong> irrigation.<br />
In Iran like some <strong>of</strong> the developing countries, there is not a clear understanding about role <strong>of</strong> the new methods<br />
<strong>of</strong> irrigation in sustainable water management in agriculture sector and policy makers have difficulty in<br />
prioritizing the policies and strategies. In this regard, public involvement will enhance and accelerate the<br />
adoption process.<br />
REFERENCES<br />
Ashley, R., Blackwood, D., Butler, D., Davies, J., Jowitt, P., & Smith, H. (2003). Sustainable decision making<br />
for UK water industry. Engineering Sustainability, 1, 41-49.<br />
Bonati, G., and Gelb, E. (2005) 'Evaluating internet for extension in agriculture.' In: gelb, B. And Offer, A.<br />
(ed.), ICT in Agriculture: Perspectives <strong>of</strong> Technological Innovation, Paris: European Federation for<br />
Information Technologies in Agriculture, Food and the Environment.<br />
Chizari, M., Karbasioun, M., and Lindner, J.R. (1998). Obstacles facing extension agents in the development<br />
and delivery <strong>of</strong> extension educational programs for adult farmers in the Province <strong>of</strong> Esfahan, Iran.<br />
<strong>Journal</strong> <strong>of</strong> Agricultural Education, 1, 48-54.<br />
Evenson, R. (1997). The economic contributions <strong>of</strong> agricultural extension to agricultural and rural development.<br />
In Food and Agriculture Organization <strong>of</strong> the United Nations (eds.) Improving agricultural extension.<br />
FAO. Rom. pp. 27–36.<br />
Guterstam, B. (2008). Toward Sustainable Water Resource Management in Central Asia. [on-line]<br />
Available:www.water.tkk.fi/English/wr/research/global/material/CA_chapters/02-CA_Waters-<br />
Guterstam.pdf<br />
Karami, E., Rezaei-Moghaddam, K., & Ebrahimi, H. (2006). Predicting sprinkler irrigation adoption:<br />
Comparison <strong>of</strong> models. <strong>Journal</strong> <strong>of</strong> <strong>Science</strong> and Technology <strong>of</strong> Agricultural and Natural Resources, 1,<br />
90–104.<br />
Keshavarz, A. (2000). Recommendation on policies and programs about water and irrigation in Iran. Tehran:<br />
Agricultural Extension Organization.<br />
Keshavarz, A., Heydari, N., and Ashrafi, S. (2003). Management <strong>of</strong> agricultural water consumption, drought,<br />
and supply <strong>of</strong> water for future demands. pp. 42–48. In: Proceedings <strong>of</strong> the Seventh International<br />
Conference on the Development <strong>of</strong> Dryland, September 14–17, 2003, Tehran, Iran.<br />
Okunade, E.O. (2007). Effectiveness <strong>of</strong> extension teaching methods in acquiring knowledge, skills and attitude<br />
by women farmers in Osun State. <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong> Research, 4, 282-286.<br />
Ommani, A. R., Chizari, M., Salmanzadeh, C., & Hosaini, J. (2009). Predicting Adoption Behavior <strong>of</strong> Farmers<br />
Regarding On-Farm Sustainable Water Resources Management (SWRM): Comparison <strong>of</strong> Models.<br />
<strong>Journal</strong> <strong>of</strong> Sustainable Agriculture, 5, 595- 616.<br />
Ommani, A.R., & Noorivandi, A. (2003). Water as food security resource (Crises and Strategies). Jihad Monthly<br />
Scientific, Social and Economic Magazine, 255, 58–66.<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Sohail, M., and Cavill, S. (2006). Ethics: making it the heart <strong>of</strong> water supply. Civil Engineering, 5, 11-15.<br />
UNDP. (2007). Human Development Report 2007/2008. [on-line] Available: Http://hrd.undp.org<br />
Vojdani, M. (2006). Assessing factors influencing the adoption <strong>of</strong> irrigation technologies by farmers in<br />
Township <strong>of</strong> Bahar. Master Thesis in Agricultural Extension and Education, Tehran, Iran.<br />
World Bank. (2009). Water Resource Management. [on-line] Available :<br />
http://web.worldbank.org/WBSITE/EXTERNAL/TOPICS/EXTWAT/0,,contentMDK:21630583~men<br />
uPK:4602445~pagePK:148956~piPK:216618~theSitePK:4602123,00.html<br />
Main Occupation Farming and Gardening (44%) Gardening (24.0%)<br />
Age (year) Mean=46<br />
Work Experience (Year) Mean=19<br />
Educational level Secondary School (75%) Diploma (25%)<br />
Amount <strong>of</strong> land owned (Hectares) Mean= 10.5<br />
Table 1. Personal Characteristics <strong>of</strong> Respondents.<br />
Sources Mean and Standard Deviation<br />
15<br />
Mean SD<br />
Extension Agents 3.58 0.959<br />
Rural Cooperatives 2.77 0.886<br />
Agricultural Magazines 2.55 1.347<br />
Agricultural Input suppliers 2.43 0.890<br />
Local Leaders 2.31 1.056<br />
Neighbors 2.13 0.824<br />
Rural Service Centers 2.09 0.928<br />
Relatives 1.67 0.864<br />
Experiment Stations 1.59 1.783<br />
Table 2. Means <strong>of</strong> respondents’ views about the sources which help them to acquire information about sprinkler<br />
irrigation system (1=Too little; 5=Too much).
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Communication Channels Mean and Standard Deviation<br />
Extension Agents 3.80<br />
Television 3.58<br />
Visit the sample farm 3.09<br />
16<br />
Mean SD<br />
1.069<br />
0.959<br />
0.963<br />
Rural organizations 2.77 0.886<br />
Printing Materials 2.63 1.178<br />
Private Sector 2.41 0.881<br />
Local Leaders 2.31 1.563<br />
Radio 2.18 1.063<br />
Neighbors 2.13 0.824<br />
Researchers 2.08 0.900<br />
Relatives 1.67<br />
0.864<br />
Table 3. Means <strong>of</strong> respondents’ views about the role communication channels which influence the adoption <strong>of</strong><br />
sprinkler irrigation systems by gardeners (1=strongly disagree; 5=strongly agree).<br />
ٍ Extension Mechanisms Mean and Standard Deviation<br />
Visiting extension agents in service centers 3.18<br />
Extension Classes 3.17<br />
Visit the sample farm 2.96<br />
Mean SD<br />
1.032<br />
1.042<br />
1.021<br />
Extension films 2.81 1.024<br />
Visiting extension agents in the field 2.78 1.041<br />
Workshops 2.57 1.057<br />
Table 4. Means <strong>of</strong> respondents’ views about the role <strong>of</strong> extension mechanisms in adopting sprinkler irrigation<br />
systems by gardeners (1=strongly disagree; 5=strongly agree).<br />
Independent variables Dependent variable Gardeners<br />
r Sig.<br />
Age Adoption <strong>of</strong> Sprinkler Irrigation System 0.535 0.000**<br />
Workshop Adoption <strong>of</strong> Sprinkler Irrigation System 0.050 0.550<br />
Visiting Extension Agents in service centers Adoption <strong>of</strong> Sprinkler Irrigation System 0.329 0.021*<br />
Working Experience Adoption <strong>of</strong> Sprinkler Irrigation System 0.519 0.000**<br />
Extension Classes Adoption <strong>of</strong> Sprinkler Irrigation System 0.315 0.025*<br />
Visiting the Sample Farm Adoption <strong>of</strong> Sprinkler Irrigation System 0.327 0.020*<br />
Extension films Adoption <strong>of</strong> Sprinkler Irrigation System 0.094 0.562<br />
Visiting extension agents in the field Adoption <strong>of</strong> Sprinkler Irrigation System 0.306 0.031*<br />
**p
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
B Beta T Sig.<br />
Constant 0.402 ------- 0.792 0.434<br />
Visiting extension agents in service<br />
centers<br />
0.414 0.386 4.327 0.000<br />
Extension classes 0.226 0.284 3.086 0.004<br />
Visiting extension agents in field 0.197 0.240 2.963 0.005<br />
Visiting the sample farm 0.210 0.292 2.750 0.010<br />
R 2 =0.45<br />
Table 6. Multivariate Regression Analysis (adopting the sprinkler irrigation system as dependent variable).<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
GEOELECTRIC ASSESSMENT OF GROUNDWATER PROSPECT AND<br />
VULNERABILITY OF OVERBURDEN AQUIFERS AT IDANRE, SOUTHWESTERN<br />
NIGERIA<br />
OMOSUYI, G.O.<br />
Department <strong>of</strong> <strong>Applied</strong> Geophysics, Federal University <strong>of</strong> Technology,<br />
P.M.B. 704, Akure, Nigeria<br />
E-mail address for correspondence : droluomosuyi@yahoo.com<br />
___________________________________________________________________________________________<br />
Abstract: Idanre and environs, southwestern Nigeria, is characterized by extensive outcrops <strong>of</strong> crystalline<br />
basement rocks, largely <strong>of</strong> granite gneiss petrology. Inadequate municipal water supply, coupled with<br />
hydrogeologically difficult nature <strong>of</strong> the terrain, individuals and corporate bodies indiscriminately sink tube wells<br />
and boreholes within the unconsolidated overburden materials, with glaring lack <strong>of</strong> concerns for the vulnerability<br />
status <strong>of</strong> aquifers, and possible environmental risk. Sixty five (65) Schlumberger depth sounding data from the<br />
area were interpreted in order to assess the groundwater prospect, focused on the thickness <strong>of</strong> the unconsolidated<br />
materials overlying the crystalline bedrock. The resistivity parameter <strong>of</strong> the geoelectric topmost layer across the<br />
area was also used to assess the vulnerability <strong>of</strong> the underlying aquifers to near-surface contaminants. The<br />
thickness <strong>of</strong> the unconsolidated overburden varies from 0.5m to 15.8m, where about 81.5% falls within the 1-5.9m<br />
brackets. This shows that unconsolidated materials are generally not significantly thick and hence <strong>of</strong> apparently<br />
low groundwater prospect. The topmost geoelectric layer has resistivity mostly within the range <strong>of</strong> 1-100 Ohm-m<br />
(77%) across the area. Resistivity values within these brackets tend to indicate silt or clay sequence, which can<br />
constitute effective protective geologic barriers for the underlying aquifers. This suggests that aquifers within the<br />
unconsolidated overburden at Idanre are mostly capped by impervious/semi-pervious materials, geologically<br />
protecting the underlying aquifers from near-surface contaminants.<br />
___________________________________________________________________________________________<br />
INTRODUCTION<br />
Groundwater has become immensely important for human water supply in urban and rural areas in developed and<br />
developing nations alike. Despite its importance, there is gross inadequate supply <strong>of</strong> water at Idanre, the study<br />
area.<br />
Idanre lies within the Precambrian basement complex terrain <strong>of</strong> southwestern Nigeria (Rahaman, 1988).The<br />
crystalline basement rocks are extensively exposed in the area (Ocan, 1991). In basement terrains, groundwater is<br />
generally believed to occur within the overlying unconsolidated material derived from the in-situ weathering <strong>of</strong><br />
rocks, and the fractured/faulted bedrock (Clark, 1985; Jones, 1985; Acworth, 1987; Bala and Ike, 2001). Since the<br />
intrinsic resistivity <strong>of</strong> the unconsolidated overburden and that <strong>of</strong> the crystalline basement differs by orders <strong>of</strong><br />
magnitude, geoelectric methods are suitable to map the thickness and extent <strong>of</strong> the overburden (1975; Koefoed,<br />
19
1989; Parasnis, 1997). The electrical resistivity depth sounding is useful in locating areas <strong>of</strong> maximum aquifer<br />
thickness and serves as a good predictive tool for estimation <strong>of</strong> borehole depth.<br />
Aquifers in basement complex terrains <strong>of</strong>ten occur at shallow depths, thus exposing the water within to<br />
environmental risks, that is, vulnerable to surface or near-surface contaminants. A recent study (Omosehin, 2009)<br />
reveals that the people around Idanre abstracts water from the unconsolidated materials overlying the crystalline<br />
basement through uncontrolled sinking <strong>of</strong> tube wells, with glaring lack <strong>of</strong> concern for aquifer vulnerability to<br />
near-surface contaminants and quality status <strong>of</strong> the groundwater.<br />
This work, in addition to assessing the groundwater prospect <strong>of</strong> the unconsolidated materials in the area, the<br />
geoelecrtic parameters <strong>of</strong> the near-surface materials overlying the aquifers were also used to assess the<br />
vulnerability <strong>of</strong> the near-surface aquifers to near-surface contaminants. The work is anticipated to upgrade our<br />
knowledge on groundwater potential <strong>of</strong> the unconsolidated material in the area, and the vulnerability <strong>of</strong> the<br />
aquifers within.<br />
Geologic setting<br />
Idanre area is underlain by the Precambrian basement complex <strong>of</strong> southwestern Nigeria (Ajibade and Fitches,<br />
1988), where six major petrologic units has been identified and described by Rahaman (1988). The study area is<br />
underlain by three <strong>of</strong> these six major petrologic units: the migmatite gneisses, members <strong>of</strong> the older granite suite<br />
and charnockitic rocks (Ocan, 1991). Most <strong>of</strong> the outcrops observed in Idanre are melanocratics, therefore<br />
possibly rich in biotite and/or hornblende. Field observation shows that granite rocks constitute extensive outcrops<br />
in the entire area (Fig 1). Granite gneisses outcrops either occur alone or in association with other components.<br />
Minerallogically, the granite gneiss around Idanre are composed <strong>of</strong> alkaline feldspar, quartz, plagioclase and<br />
biotite (Ocan, 1991).<br />
Materials and Methods <strong>of</strong> study<br />
The vertical electrical soundings (VES) were conducted using the Schlumberger electrode array (Zhody et al.,<br />
1974). The Ohmega Resistivity Meter was used for resistance measurement. The geoelectric survey comprised <strong>of</strong><br />
sixty five (65) depth soundings (Fig 2), with maximum current electrode spacing (AB) ranging from 130m to<br />
200m (AB/2 = 65 - 100). The field curves were interpreted through partial curve matching (Koefoed, 1979),<br />
engaging master curves and auxiliary point charts (Orellana and Mooney, 1966).<br />
20
5 00' E<br />
7 15' N<br />
7 15' N<br />
River Osun<br />
River Apurare<br />
River Owena<br />
5 00' E<br />
Owena<br />
60<br />
50<br />
Ago - M<strong>of</strong>erere<br />
Gberiwojo<br />
Ago - Ireti<br />
Aponmu Akore<br />
Odoko Bekun Odoji<br />
ALADE<br />
IDANRE<br />
Odo - Isa<br />
Odo - Isa<br />
21<br />
Apefon<br />
Igbo - Olokun<br />
Igbo - Epo - Aiyem<strong>of</strong>ewa<br />
Omiwonja<br />
Ajegunle - Arun<br />
Iwanja - M<strong>of</strong>erere<br />
Igbo - Epo<br />
Igbo - Epo - Owom<strong>of</strong>ewa<br />
300 m<br />
0<br />
River Aponmu<br />
River Esun<br />
A<br />
50<br />
40<br />
River Iwari<br />
River Imoja<br />
Porphyritic Granites<br />
Massive charnockite<br />
Granitic charnockite<br />
Migmatite<br />
Strike and dip <strong>of</strong> Foliation<br />
Major fault<br />
Idanrore<br />
Tejugbala<br />
Ajegunle - Iwonja<br />
B<br />
1 0 1 2 3 4 5 Km<br />
0 2000 4000 6000 8000 10000 12000<br />
LEGEND<br />
ALADE River Arun<br />
20<br />
A<br />
Cross Section Across Direction A - B<br />
River Ogburugburu<br />
Opa - Idanre<br />
Kajola - Asoko<br />
River Owena<br />
Oposinle<br />
River Otan<br />
AKURE<br />
Orientation Of feldspar in granite<br />
Roads<br />
Footpaths<br />
Village<br />
Fig. 1: Simplified Geological Map around Idanre (Ocan, 1991).<br />
50<br />
60<br />
River<br />
40<br />
20<br />
40<br />
Italepo - Odo<br />
Ododin Ipinlerere<br />
B<br />
30<br />
30<br />
Oda<br />
Oke - Alafia<br />
5 15' E<br />
5 15' E<br />
7 15' N<br />
7 00' N
The manually derived geoelectric parameters were subjected to an inversion (Vander Velpen, 1988), which<br />
successfully reduced the interpretation error to acceptable levels (Barker, 1989).<br />
The electrical resistivity contrasts existing between lithological sequences in the subsurface (Dodds and Ivic, 1998;<br />
Lashkaripour, 2003) were used in the delineation <strong>of</strong> geoelectric layers, identification <strong>of</strong> aquiferous materials<br />
(Deming, 2002) and assessment <strong>of</strong> groundwater prospect <strong>of</strong> the area. Also, the resistivity parameter <strong>of</strong> the<br />
uppermost geoelectric layer (topsoil) was used to evaluate, in quantitative terms, its permeability to surface/nearsurface<br />
contaminants, and hence the vulnerability <strong>of</strong> the underlying aquifers, as demonstrated in Draskovits et al.<br />
(1995).<br />
7 06' 27.4''<br />
7 06' 22.3'' 5 06' 15.0''<br />
v54<br />
o<br />
T<br />
A<br />
e<br />
r u<br />
k<br />
v53<br />
v51<br />
v52<br />
v1<br />
v3<br />
v2<br />
v7<br />
v4<br />
o<br />
r v6 v5<br />
l v8<br />
v11 v12<br />
a<br />
d<br />
v9<br />
v10<br />
v13<br />
v37<br />
v14<br />
v33 v36 v19 v18<br />
v15<br />
v35<br />
v32<br />
v17<br />
v16<br />
v27<br />
v26 v31 v34<br />
v25 v30<br />
v20<br />
v23 v21<br />
v28 v24<br />
v29<br />
v22<br />
v38<br />
v42<br />
v41<br />
v39<br />
v40<br />
v43 v44 v45 v46 v47<br />
m<br />
m<br />
o<br />
C<br />
v49 v48<br />
v50<br />
e r c i a<br />
T o A p e f o n<br />
T o A b a B a b u b u<br />
Scale<br />
0 1000 2000<br />
Fig. 2: Layout Map <strong>of</strong> Idanre showing VES positions (Inset: Map <strong>of</strong> Nigeria).<br />
m<br />
v59<br />
22<br />
v57<br />
v58<br />
v56<br />
v60 v61 v62 v63<br />
v65<br />
v64<br />
v55<br />
T o<br />
l<br />
S c<br />
h<br />
l a<br />
i c<br />
n<br />
T e c<br />
h .<br />
T o A p e t a n<br />
5 08' 22.3''<br />
Study Area<br />
N<br />
NIGERIA<br />
v<br />
LEGEND<br />
Road / Major Street<br />
Minor Street<br />
VES Location<br />
River<br />
Scale<br />
0 300 Km
RESULTS AND DISCUSSIONS<br />
The Schlumberger depth soundings produced a short range <strong>of</strong> sounding curves: three-layer case <strong>of</strong> type A (41.5%),<br />
H type (24.6%), and four-layer curves <strong>of</strong> type KH (15.4%) were mostly recorded. Typical curves are shown in Fig<br />
3. Field curves <strong>of</strong>ten mirror-image (geoelectrically) the nature <strong>of</strong> the successive lithologic sequence in a place and<br />
hence can be used, in qualitative sense, to assess the groundwater prospect <strong>of</strong> an area (Worthington, 1977). Type<br />
H and KH curves are <strong>of</strong>ten associated with groundwater possibilities while type A may typify a rapid resistivity<br />
progression, indicative <strong>of</strong> shallow, resistive bedrock.<br />
Aquifer Delineation: Electrical resistivity contrasts exists across interfaces <strong>of</strong> lithologic units in the subsurface.<br />
These contrasts are <strong>of</strong>ten adequate to delineate discrete geoelectric layers and identify aquiferous or nonaquiferous<br />
layers (Schwarz, 1988). The geoelectric parameters <strong>of</strong> the aquifer units were determined from the<br />
interpretation <strong>of</strong> the sounding curves. Resistivity <strong>of</strong> earth materials is strongly affected by water saturation and<br />
water quality (Lucius et al., 2001). The resistivity parameter <strong>of</strong> a geoelectric layer is an important factor to<br />
adjudge an aquifer or otherwise.<br />
Cross sections <strong>of</strong> interpreted resistivity data from the area (Fig 4) show three to four geoelectric layers: the topsoil,<br />
the lateritic or weathered layer, and the fractured/fresh bedrock. In the topsoil, resistivity values range from 20 to<br />
260 Ohm-m, with layer thickness varying between 0.5 and 2.1m. The lateritic or weathered layer has resistivity in<br />
the range <strong>of</strong> 35 to 600 Ohm-m, with most <strong>of</strong> the values (67%) less than 150 Ohm-m. Layer thickness ranges from<br />
0.8 to 7.8m. In few areas however, the thickness gets up to over 20m, but about 85% <strong>of</strong> layer thickness obtained is<br />
less than 6m. The presumed decomposed portion <strong>of</strong> the bedrock has resistivity in the range <strong>of</strong> 69 to 874 Ohm-m,<br />
while the thickness ranges from 3.2 to 24m.<br />
NORTH<br />
DEPTH (m)<br />
-1<br />
-3<br />
-5<br />
-7<br />
-9<br />
-11<br />
-13<br />
-15<br />
-17<br />
(a)<br />
VES 54<br />
61<br />
150Ohm-m<br />
8121<br />
Depth (m)<br />
4<br />
2<br />
33<br />
Scale<br />
0<br />
0 400<br />
Distance (m)<br />
VES 3<br />
VES 11 VES 38<br />
VES 8 VES 42<br />
99<br />
31<br />
54694<br />
22<br />
197<br />
2522<br />
114<br />
23<br />
299<br />
103<br />
5683<br />
59<br />
27<br />
599<br />
73<br />
54 Ohm-m<br />
1199<br />
LEGEND<br />
VES 25 VES 29<br />
79<br />
26<br />
9233<br />
Topsoil<br />
67<br />
109<br />
24<br />
1175 Ohm-m<br />
590<br />
7251<br />
Weathered layer<br />
Fractured basement<br />
Fresh basement<br />
SOUTH
DEPTH (m)<br />
WEST<br />
0<br />
-2<br />
-4<br />
-6<br />
-8<br />
-10<br />
-12<br />
-14<br />
VES 43<br />
88<br />
VES 44<br />
83 Ohm-m<br />
8868<br />
(b)<br />
66<br />
159<br />
26840<br />
Depth (m)<br />
VES 45 VES 27 VES 26 VES 31<br />
4<br />
2<br />
64<br />
79<br />
8284<br />
Scale<br />
0<br />
0 300 600<br />
Distance (m)<br />
22<br />
119<br />
23<br />
12742<br />
24<br />
60<br />
38<br />
351<br />
1206<br />
13<br />
891<br />
Fig 4(a) & (b): Cross Sections <strong>of</strong> Interpreted Resistivity data from Idanre.<br />
Assessment <strong>of</strong> Groundwater Prospect<br />
VES 34<br />
26<br />
3172 Ohm-m<br />
221<br />
1553<br />
LEGEND<br />
Topsoil<br />
Weathered layer<br />
Fractured basement<br />
Fresh basement<br />
VES 17<br />
No acceptable framework has yet emerged, as to where exactly is the major focus for groundwater resources in a<br />
typical crystalline basement terrain. Acworth (1987) reported successful completion <strong>of</strong> boreholes in shallow<br />
weathered zones in a typical basement terrain. Fracture-zone aquifers in crystalline rocks are also believed to be<br />
important sources <strong>of</strong> water for rural communities (Meju et al., 1999). Lenkey et al (2005) however believes that<br />
the thickest layer above the basement constitute the main water-bearing layer.<br />
The approach <strong>of</strong> Lenkey et al (2005) has been adapted for this study. Fig 5 is a contour map while figure 6 is the<br />
numerical value distribution, showing the thickness <strong>of</strong> unconsolidated materials overlying the crystalline<br />
basement in Idanre; the thickness ranges from 0.5m to 15.8m, with an average <strong>of</strong> 4.5m. Fig 5 shows that<br />
overburden thickness <strong>of</strong> 1-5.9m in the area constitutes about 81.5%, thus suggesting that the water-bearing<br />
horizon (Lenkey et al., 2005) across the area is generally not significantly thick.<br />
Assessment <strong>of</strong> Aquifer Vulnerability<br />
Due to shallow depth <strong>of</strong> occurrence, aquifers in crystalline basement terrains are <strong>of</strong>ten exposed to environmental<br />
risks. An effective groundwater protection is given by protective geologic barriers with sufficient thickness<br />
(Mundel et al., 2003) and low hydraulic conductivity. Laterite, silt or clay <strong>of</strong>ten constitutes protective geologic<br />
barriers. When found above an aquifer they constitute its cover (Lenkey et al., 2005).<br />
The resistivity parameters <strong>of</strong> the uppermost geoelectric layer in the study area have been used to assess the<br />
vulnerability <strong>of</strong> the underlying aquifers. Fig 7 is a contour map <strong>of</strong> resistivity <strong>of</strong> the first layer while figure 8 shows<br />
the numerical resistivity distribution across the first layer in the area.<br />
35<br />
56<br />
12480<br />
EAST
7 06' 27.4''<br />
7 06' 22.3''<br />
Frequency<br />
v53<br />
v54<br />
v51<br />
v52<br />
v1<br />
v3<br />
v2<br />
v7<br />
v4<br />
v8 v6 v5<br />
v11v12 v9<br />
v42<br />
v10<br />
v37<br />
v13<br />
v14<br />
v15<br />
v33 v36<br />
v19v18<br />
v35<br />
v32<br />
v17<br />
v16<br />
v27<br />
v26 v31<br />
v34<br />
v25 v30<br />
v20<br />
v23 v21<br />
v28 v24<br />
v29<br />
v22<br />
v38<br />
v49 v48<br />
v50<br />
v41<br />
v39<br />
v43 v46<br />
v44v45<br />
v47<br />
v40<br />
To Aba Babubu<br />
5 06' 15.0''<br />
To Akure<br />
Commercial road<br />
Scale<br />
To Apefon<br />
0 1000 2000 m<br />
25<br />
v65<br />
v59<br />
v58<br />
v57<br />
v64<br />
v60v61v63<br />
v62<br />
v56<br />
v55<br />
To Technical Schl.<br />
To Apetan<br />
N<br />
5 08' 22.3''<br />
Fig. 5: Map <strong>of</strong> thickness <strong>of</strong> unconsolidated material overlying the Basement at Idanre.<br />
30<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
1 - 2.9 3 - 5.9 6 - 8.9 9 - 11.9 12 - 14.9 15 -17.9<br />
Overburden Thickness (m)<br />
Fig 6: Distribution <strong>of</strong> thickness <strong>of</strong> unconsolidated material at Idanre.<br />
v<br />
Series1<br />
22 m<br />
19<br />
16<br />
13<br />
10<br />
7<br />
4<br />
1<br />
LEGEND<br />
Road / Major Street<br />
Minor Street<br />
VES Location
7 06' 27.4''<br />
7 06' 22.3''<br />
Frequency<br />
v53<br />
v54<br />
v51<br />
v52<br />
v1<br />
v3<br />
v2<br />
v7<br />
v4<br />
v8 v6 v5<br />
v11v12 v9<br />
v42<br />
v10<br />
v37<br />
v13<br />
v14<br />
v15<br />
v33 v36<br />
v19v18<br />
v35<br />
v32<br />
v17<br />
v16<br />
v27<br />
v26 v31<br />
v34<br />
v25 v30<br />
v20<br />
v23 v21<br />
v28 v24<br />
v29<br />
v22<br />
v38<br />
v49 v48<br />
v50<br />
v41<br />
v39<br />
v43 v46<br />
v44v45<br />
v47<br />
v40<br />
To Aba Babubu<br />
5 06' 15.0''<br />
60<br />
50<br />
40<br />
30<br />
20<br />
10<br />
0<br />
To Akure<br />
Commercial road<br />
Scale<br />
To Apefon<br />
0 1000 2000<br />
26<br />
m<br />
v65<br />
v59<br />
v58<br />
v57<br />
v64<br />
v60v61v63<br />
v62<br />
v56<br />
v55<br />
To Technical Schl.<br />
To Apetan<br />
N<br />
5 08' 22.3''<br />
Fig. 7: Contour Map <strong>of</strong> Resistivity Distribution in the First Layer at Idanre.<br />
1-100 101-200 201-300 301-400 401-500 501-600 601-700 701-800 801-900 901-<br />
1000<br />
Resistivity (Ohm-m)<br />
Fig 8: Distribution <strong>of</strong> resistivity in the topmost geoelectric layer at Idanre<br />
Series1<br />
v<br />
800 Ohm-m<br />
750<br />
700<br />
650<br />
600<br />
550<br />
500<br />
450<br />
400<br />
350<br />
300<br />
250<br />
200<br />
150<br />
100<br />
50<br />
0<br />
LEGEND<br />
Road / Major Street<br />
Minor Street<br />
VES Location
About 77% <strong>of</strong> the resistivity values <strong>of</strong> the topmost geoelectric layer fall within 1-100 Ohm-m range. In Nigerian<br />
geological circumstances, this suggests considerable clayey or silt sequences (aquitard), with effective capacity to<br />
constitute impervious/semi-impervious barriers.<br />
CONCLUSIONS AND RECOMMENDATIONS<br />
Due to rugged geologic terrain, the unconsolidated materials overlying the crystalline basement rocks around<br />
Idanre constitute the major water-bearing horizon from which the inhabitants abstract water for domestic needs.<br />
Geoelectric depth sounding around the area reveals that the thickness <strong>of</strong> the unconsolidated materials varies from<br />
0.5m to 15.8m, where values within 1-5.9m brackets constitute about 81.5%. This indicates that the<br />
unconsolidated material in the area is not significantly thick, thus suggesting that the groundwater potential is<br />
apparently low.<br />
About 77% <strong>of</strong> the resistivity values <strong>of</strong> the topmost geoelectric layer in the area fall within the range <strong>of</strong> 1-100<br />
Ohm-m. Values <strong>of</strong> resistivity within this brackets suggest aquitard (silt or clay), which constitute effective,<br />
impervious geologic barriers to infiltrating near-surface contaminants. Aquifers within the unconsolidated<br />
materials at Idanre are therefore mostly capped by impervious/semi-pervious geologic materials, suggesting that<br />
they are mostly non-vulnerable to near-surface contaminants.<br />
Since decomposed bedrock in the crystalline basement terrain can house significant quantity <strong>of</strong> groundwater,<br />
groundwater developers in the area may explore the bedrock for bedrock aquifers, to complement the aquifers<br />
within the unconsolidated overburden.<br />
ACKNOWLEDGEMENT<br />
Messrs T. Omosehin, E. Faleye and M. Bawallah assisted in the data acquisition while Messrs O.Adegoke and A.<br />
I. Adeyemo helped in preparing the figures. The author gratefully acknowledged these assistances.<br />
REFERENCES<br />
Acworth, R.I. (1987). The development <strong>of</strong> crystalline basement aquifers in a tropical environment. Q. J. Eng. Geol.<br />
London. Vol. 20, pp. 265-272<br />
Ajibade, A.C. and Fitches, W.R. (1988). The Nigerian Precambrian and the Pan- African Orogeny. In:<br />
Precambrian Geology <strong>of</strong> Nigeria. A publication <strong>of</strong> the Geological Survey <strong>of</strong> Nigeria. Pp 329.<br />
Barker, R.D. (1989). Depth <strong>of</strong> investigation <strong>of</strong> collinear symmentrical four-electrode arrays. Geophysics 54, 1031-<br />
1037<br />
Bala, A. E. and Ike, E. C. (2001). The Aquifer <strong>of</strong> the Crystalline Basement Rocks in Gusau Area, North-Western<br />
Nigeria. <strong>Journal</strong> <strong>of</strong> Mining and Geology, Vol. 37, No. 2, pp. 177 – 184.<br />
Clark, L. (1985). Groundwater abstraction from Basement Complex areas <strong>of</strong> Africa. Q. J. Eng. Geol. London. Vol.<br />
18, pp 25-32.<br />
Deming, D. (2002). Intrduction to Hydrogeology. McGraw Hill Company. Pp 468.<br />
Dodds, A.R. and Ivic, D. (1988). Integrated geophysical methods used for groundwater studies in the Murray<br />
Basin, South Australia. In Geotechnical and Environmental <strong>Studies</strong> Geophysics, Vol II: Soc. Explor<br />
Geophys.,Tulsa, pp 303-310.<br />
27
Draskovits, P, Maayar, B and Pattantyus-A, M. (1995). Geophysical methods in groundwater prospecting and<br />
environmental protection. Fisica de la Tierra, no 7, 53-86.<br />
Lones, M.J. (1985). The weathered zone aquifers <strong>of</strong> the basement complex areas <strong>of</strong> Africa. Q. J. Eng. Geol.<br />
London. Vol. 18, pp 35-46.<br />
Koefeod, O. (1979). Geosounding Principles, 1. Resistivity sounding measurements. Elsevier Scientific<br />
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Lenkey, L., Hamori, Z and Mihalffy, P. (2005). Investigating the hydrogeology <strong>of</strong> a water-supply area using<br />
direct-current vertical electrical soundings. Geophy, Vol.70. no. 4, H1-H19<br />
Lashkarripour, G.R. (2003). An investigation <strong>of</strong> groundwater condition by geoelectrical resistivity method: A case<br />
study in Korin aquifer, southeast Iran. <strong>Journal</strong> <strong>of</strong> Spatial Hydrology, Vol.3, No. 1, pp1-5.<br />
Lucius, J.E., Bisdort, R. J. and Abraham, J. (2001). Results <strong>of</strong> electrical survey near Red River, New Mexico.<br />
USGS Open-File Report 01-331, pp24.<br />
Meju, M.A., Fontes, S.L., Oliveira, M.F.B., Lima, J.P.R., Ulugerger, E.U. and Carrasquilla, A.A. (1999). Regional<br />
aquifer mapping using combined VES-TEM-AMT?EMAP methods in the semiarid eastern margin <strong>of</strong><br />
Parnaiba Basin, Brazil. Geophysics, Vol. 64, No. 2. P. 337-356.<br />
Mundel, J.A., Lother, L., Oliver, E.M. and Allen-Long, S. (2003). Aquifer vulnerability analysis for Water<br />
Resources Protection. Indiana Department <strong>of</strong> Environmental Management (IDEM), ‘Source Water<br />
Assessment Plan’, pp 25.<br />
Ocan, T. (1990). Petrogenesis <strong>of</strong> the rock units <strong>of</strong> Idanre, southwestern Nigeria. Unpublished Ph.D thesis,<br />
Obafemi Awolowo University, Ile Ife, Nigeria, pp 194.<br />
Omosehin, T.B. (2008). Geoelectric delineation <strong>of</strong> aquifers and assessment <strong>of</strong> their vulnerability in Idanre,<br />
Southwestern Nigeria. Unpublished M. Tech. thesis, Federal University <strong>of</strong> Tech., Akure, Nigeria. Pp 83.<br />
Orellana, E. and Mooney, H.M. (1966). Master tables and curves for vertical electrical<br />
sounding over layered structures. Inteciencis, Madrib, 34pp.<br />
Parasnis, D.S. (1979). Principles <strong>of</strong> <strong>Applied</strong> Geophysics. Chapman and Hill, London. Pp 98 130.<br />
Rahaman, M.A. (1988). Recent advances in the study <strong>of</strong> the Basement complex <strong>of</strong> Nigeria. Precambrian Geology<br />
<strong>of</strong> Nigeria. A Publication <strong>of</strong> Geological Survey <strong>of</strong> Nigeria. Pp. 11-41.<br />
Schwarz, S.D. (1988). Application <strong>of</strong> Geophysical Methods to Groundwater Exploration in the Tolt River Basin,<br />
Washington State. In Geotechnical and Environmental Geophysics. Vol 1. Soc. Explor. Geophs, Tulsa,<br />
pp 213-217.<br />
Vander Velpen, B. P. A. (1988). Resist Version 1.0, M.Sc. Research Project, ITC. Delft, Netherlands.<br />
Worthington, P. R. (1977). Geophysical investigations <strong>of</strong> groundwater resources in the Kalahari Basin.<br />
Geophysics, Vol. 42, No 4, pp.838-849.<br />
Zohdy, A. A. R., Eaton, G. P., and Mabey, D. R. (1974). Application <strong>of</strong> surface geophysics to groundwater<br />
investigations: Techniques <strong>of</strong> water resources investigations <strong>of</strong> U.S. Geol. Survey: Book 2, Chapter DI,<br />
U.S. Government Printing Office, Washington, pp.66.<br />
28
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Comparative vegetative and foliar epidermal features <strong>of</strong> three Paspalum L. species in<br />
Edostate, Nigeria.<br />
E.A Ogie-Odia*, A.I Mokwenye*, O. Kekere ** and O. Timothy ***<br />
*Department <strong>of</strong> Botany, Ambrose Alli University, Ekpoma , Edo State.<br />
** Department <strong>of</strong> Plant <strong>Science</strong> and Biotechnology, Adekunle Ajasin University, Akungba Akoko, Ondo State.<br />
*** Department <strong>of</strong> Environmental <strong>Science</strong>, Western Delta University, Oghara, Delta State.<br />
*Email address for correspondence: effexing@yahoo.com<br />
___________________________________________________________________________________________<br />
Abstract: Investigations into the vegetative morphology and epidermal features <strong>of</strong> three species <strong>of</strong> the genus<br />
Paspalum L. (P. conjugatum Berg, P. scrobiculatum L. and P. vaginatum Sw.) was carried out. Pictorial<br />
illustrations are presented. For the vegetative features, it was observed that there is variability <strong>of</strong> hairs on both the<br />
margins <strong>of</strong> the lamina and leaf sheath <strong>of</strong> P. scrobiculatum. In the epidermal studies, macro-hairs were observed on<br />
the margins <strong>of</strong> the lamina <strong>of</strong> two out <strong>of</strong> the three taxa; prickles were observed on the intercoastal zone <strong>of</strong> two out <strong>of</strong><br />
the three taxa; papillae was observed in the intercoastal zone <strong>of</strong> one <strong>of</strong> the three taxa; micro-hairs were observed in<br />
two out <strong>of</strong> the three taxa. It was observed that the shape <strong>of</strong> the subsidiary cells <strong>of</strong> P. conjugatum varied from low<br />
dome to triangular in the adaxial surface and mainly triangular shaped in the abaxial surface. P.scrobiculatum had<br />
mainly triangular shaped subsidiary cells, while that <strong>of</strong> was low dome shaped in the adaxial surface and triangular<br />
shaped in the abaxial surface. On the basis <strong>of</strong> the variations that exist in its morphological and epidermal features, a<br />
taxonomic key has been produced for identification and separation <strong>of</strong> the various taxa.<br />
Keywords: Vegetative, leaf epidermal, genus, Paspalum, Poaceae, systematic.<br />
___________________________________________________________________________________________<br />
INTRODUCTION<br />
Poaceae which is the grass family includes approximately 10,000 species classified into 600 to 700 genera (Clayton<br />
and Renvoize, 1986). The grasses are included with lilies, Orchids, Pineapples and Palms in the group known as<br />
monocotyledons which includes all flowering plants with a single seed leaf (Kellogg, 2001). The members <strong>of</strong> this<br />
group are present in all the conceivable habitats, suitable for growth <strong>of</strong> plant communities (Mitra and Mukherjee,<br />
2005). The grass family Poaceae, is noted for its wide diversity and complexity and so has posed many problems to<br />
the taxonomists using the traditional methods based on gross morphology (Strivastava, 1978).<br />
Before the later part <strong>of</strong> the 19 th century, taxonomists were confined to the use <strong>of</strong> the features <strong>of</strong> reproductive organs<br />
as floral characters were considered to provide the most valuable characters to taxonomic affinities (Nwokeocha,<br />
1996). Of all the non-reproductive organs, the leaf is the most widely used in plant taxonomy (Stace, 1984).<br />
Strivastava (1978) described the leaf epidermis as the second most important character after cytology for solving<br />
taxonomic problems.<br />
29
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Paspalum L. is a member <strong>of</strong> the tribe Paniceae R. Br. Within the Paniceae, Paspalum is one <strong>of</strong> the most complex<br />
genera containing over 400 species that are largely endemic to the tropics and subtropics <strong>of</strong> the world (Clayton and<br />
Renvoize, 1986). The centre <strong>of</strong> diversity <strong>of</strong> this genus is South America (Fernandes et al, 1968). In Nigeria, Lowe<br />
(1989) reported that the genus is represented by five species which are mostly straggling plants grown in damp open<br />
places. The reported species are P. vaginatum, P. conjugatum, P. notatum, P. scrobiculatum and P. auriculatum.<br />
The economic values <strong>of</strong> these species are many. For example, P. vaginatum provides for dune stabilization and<br />
waterflow fodder under saline and fresh water environments respectively and can also be cultivated as a turfgrass for<br />
soil stabilization. On the other hand, P. scrobiculatum has been domesticated as a cereal grain in Asia (Jarret et al.,<br />
1998). The use <strong>of</strong> morphological and leaf epidermal features has been found to be <strong>of</strong> immense interest in taxonomy.<br />
An excellent review <strong>of</strong> the application <strong>of</strong> morphological features in systematic studies is shown in the works <strong>of</strong><br />
Olowokudejo 1990, Mensah and Gill (1997), Edeoga and Ikem 2001, Gill and Mensah (2001) and Kharazian<br />
(2007).The use <strong>of</strong> leaf epidermal features in systematics has become popular and distinctive and has been used as a<br />
great taxonomic tool at the levels <strong>of</strong> family, genus and species.<br />
This study is to give the morphological description <strong>of</strong> the three Paspalum species and also to compare/determine the<br />
intraspecific relationship and patterns <strong>of</strong> variation associated with the epidermal features/characteristics among the<br />
taxa studied.<br />
METHODOLOGY<br />
Fresh and matured leaves <strong>of</strong> Paspalum scrobiculum L. and Paspalum conjugatum Berg. were collected from<br />
Beverly-Hills area, <strong>of</strong>f Benin-Auchi express road, Ekpoma, while Paspalum vaginatum Sw. was collected close to<br />
the bank <strong>of</strong> the Ikpoba river in Benin-city, Edo State. They were first boiled in water to restore to their normal<br />
shape. The tissue above the epidermis was gradually scraped away with a safety razor blade and during this<br />
operation the leaf was continuously irrigated with commercial Jik. The epidermal peels were then washed in water,<br />
stained with 1% safranin solution in 50% alcohol and temporary mounts (under low and high power) viewed under<br />
the microscope. Photo micrographs <strong>of</strong> the epidermal features were taken from the slides using a Light microscope<br />
fitted with a Cannon digital camera (5.0 mega pixels). The terminologies for the epidermal morphology are that <strong>of</strong><br />
Metcalfe (1960) and Van Cottem (1973).<br />
RESULTS<br />
The morphological (vegetative) features <strong>of</strong> the three Paspalum species investigated are summarized in Table 1. The<br />
descriptions <strong>of</strong> the leaf epidermal studies are presented in Tables 2; the epidermal and morphological Keys are also<br />
presented while the epidermal slides are illustrated in Plates 1, 2 and 3. The vegetative results <strong>of</strong> the three taxa<br />
studied showed that the habit <strong>of</strong> the three Paspalum species are perrenial herbs with P. scrobiculatum being a turfed<br />
perennial herb. The heights are about the same (60cm) with P. scrobiculatum growing up to 100cm and while <strong>of</strong> the<br />
habit and height <strong>of</strong> is perennial herb and respectively. Similarly the leaf shapes shows that they are all linear<br />
although P. conjugatum is linear lanceolate while the the inflorescence is raceme for P. conjugatum and P.<br />
vaginatum (terminal) and P. scobiculatum is digitate. The stem types varies with P. conjugatum having prostrate<br />
stoloniferous stems, P. scrobiculatum with erect or decumbent stem and P. vaginatum with creeping stoloniferous<br />
stem . Equally, all the spikelets in the three species have two rows with P. scrobiculatum and P. vaginatum being<br />
hairless while P. conjugatum has hairs.<br />
30
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 1: Vegetative characters <strong>of</strong> the three Paspalum species studied<br />
Characters Paspalum conjugatum Paspalum scrobiculatum Paspalum vaginatum<br />
Habit Perennial herb Turfed perennial herb Perennial herb<br />
Height 60cm 60-100cm 60cm<br />
Stem type Prostrate stolon Erect or decumbent Creeping stolon<br />
Leaf shape Linear or lanceolate Linear Linear<br />
Leaf texture Smooth with hairy margins S<strong>of</strong>t with rough margins and<br />
sometimes hairy<br />
31<br />
Smooth and hairless<br />
Inflorescence Raceme Digitate Terminal raceme<br />
Spikelet Two rows and hairy Two rows and hairless Two rows and hairless<br />
Ligules Toothed Distinct and short Dense<br />
Table 2: Summary <strong>of</strong> leaf epidermal features<br />
Species Surface MIC MAH PRK PAP SSc OPB Distribution<br />
<strong>of</strong> stomata<br />
Paspalum conjugatum<br />
Berg.<br />
Paspalum<br />
scrobiculatum L.<br />
Paspalum vaginatum<br />
Sw.<br />
AD C<br />
IC<br />
AB C<br />
IC<br />
AD C<br />
IC<br />
AB C<br />
IC<br />
AD C<br />
IC<br />
AB C<br />
IC<br />
-<br />
b<br />
-<br />
B<br />
-<br />
b<br />
-<br />
B<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
+<br />
-<br />
+<br />
-<br />
+<br />
-<br />
+<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
-<br />
+<br />
-<br />
-<br />
LD, T<br />
T<br />
T<br />
T<br />
LD<br />
T<br />
Db, S<br />
-<br />
S, Cr<br />
-<br />
Db, Cr<br />
-<br />
Db, Cr<br />
-<br />
HES<br />
-<br />
Db, Cr<br />
-<br />
AMP<br />
AMP<br />
AMP
Legends for Plates and Table 2<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
AB = Abaxial surface SHC = Short cell<br />
AD = Adaxial surface C = Coastal zone<br />
OPB = Opaline body LD = Low dome shaped<br />
IC = Intercoastal zone S = Saddle shaped<br />
MIC = Micro-hair Cr = Cross shaped<br />
b = Bi-cellular Db = Dumb bell shaped<br />
MAH = Macro-hair Amp = Amphistomatic<br />
PRK = Prickle HES = Horizontally elongated surface<br />
PAP = Papillae SSc = Subsidiary cell<br />
LNC = Long cell T = Triangular<br />
+ = Present - = Absent<br />
Paspalum conjugatum Berg.<br />
Leaf blade up to 9.5cm long and 6.1mm broad, with prickles and macro-hairs present on leaf margins.<br />
a. Adaxial surface: Clearly separated into coastal and intercoastal zone.<br />
Solitary short cells are present in the intercoastal zone. Long cell vary from slightly to straight anticlinal walls.<br />
Prickles present in the intercoastal zone. Bi-cellular micro-hairs with distal cell having tapering apices present in the<br />
intercoastal zone. Papillae and micro-hair were absent in the coastal and intercoastal zones. Subsidiary cells <strong>of</strong> the<br />
stomata vary from low-dome to triangular shape. Opaline bodies <strong>of</strong> the coastal zone vary from dumbbell to rounded<br />
or saddle shaped<br />
b. Abaxial surface: Clearly separated into coastal and intercoastal zone<br />
Long cells rectangular shaped with some tending to be square shaped with sinuous anticlinal walls. Long cells<br />
observed in the coastal zone. Bi-cellular micro-hairs present in the coastal zone, distal cells with tapering apices.<br />
Prickles present in the intercoastal zone. Macro-hairs and papillae absent, subsidiary cells <strong>of</strong> stomata are triangular<br />
shaped. Opaline bodies mostly saddle shaped, occasionally cross shaped in the coastal zone<br />
32
Plate 1a Adaxial surface <strong>of</strong> P. conjugatum<br />
Plate 1b Abaxial surface <strong>of</strong> P. conjugatum<br />
Paspalum scrobiculatum L.<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Leaf blade up to 16cm long and 0.9mm broad with prickles and macro-hairs present on margins.<br />
a. Adaxial surface: Clearly distinguished into coastal and intercoastal zone.<br />
Long cell are rectangular shaped with some tending to be square with sinuous walls. Solitary short cells present in<br />
the intercoastal zone. Long cells present in the coastal regions. Bi-cellular micro-hairs present in the intercoastal<br />
zone, with distal cells having tapering apices. Prickles with hook shape present in the intercoastal zone. Papillae and<br />
33<br />
C<br />
C<br />
IC<br />
PRK<br />
IC<br />
MIC<br />
SSc<br />
LNC<br />
LNC<br />
MIC<br />
SSc
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
micro-hairs absent and stomata present with triangular shaped subsidiary cells. Opaline bodies <strong>of</strong> the coastal zone<br />
are mainly cross and dumb bell shaped.<br />
b. Abaxial surface: Coastal and intercoastal zone clearly distinct.<br />
Long cells rectangular shaped with sinuous anticlinal walls. Long cells present in the coastal zone. Solitary short<br />
cells present in the intercoastal zone. Hook shaped prickles present in the intercoastal zone. Papillae and macro-hair<br />
absent, bi-cellular micro-hairs present in the intercoastal region and stomata with triangular shaped subsidiary cells.<br />
Opaline bodies vary from cross to dumb bell shaped in the coastal zone.<br />
Plate 2a Adaxial surface <strong>of</strong> P. scrobiculatum<br />
Plate 2b Abaxial surface <strong>of</strong> P. scrobiculatum<br />
Paspalum vaginatum Sw.<br />
34<br />
C<br />
C<br />
SSc<br />
IC<br />
MIC<br />
IC<br />
SSc<br />
LNC<br />
LNC<br />
MIC
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Leaf blade up to 6cm long and 2.5mm broad with prickles and macro-hairs present on margins.<br />
a. Adaxial surface: Clearly seperated into coastal and intercoastal zone.<br />
Long cell are rectangular shaped with some tending to be square with slightly sinuous to straight anticlinal walls.<br />
Short cells is absent in the intercoastal zone. Macro-hairs and micro-hairs absent, papillae tend to overarch with<br />
stomata in the intercoastal zone. Subsidiary cells <strong>of</strong> the stomata were low-dome shaped. Opaline bodies in the<br />
coastal regions are horizontally elongated.<br />
b. Abaxial surface: Clearly distinguished into coastal and intercoastal zone.<br />
Long cells are rectangular shaped with sinuous anticlinal walls in the intercoastal zone. Long cells present in the<br />
coastal zone. Short cells are paired, occasionally solitary in the intercoastal zone. Prickles, micro-hairs and macrohairs<br />
are absent. Subsidiary cells <strong>of</strong> stomata are triangular shaped.<br />
Opaline bodies vary from dumb bell to cross shaped in the coastal zone.<br />
Plate 3a Adaxial surface <strong>of</strong> P. vaginatum<br />
35<br />
C<br />
IC<br />
PAP<br />
SSc<br />
LNC
Plate 3b Abaxial surface <strong>of</strong> P. vaginatum<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Key to the three species <strong>of</strong> Paspalum studies based on their epidermal features<br />
1. Prickles present on both surfaces………………………………………………2<br />
1. Prickles absent on both surfaces……………………………………………….4<br />
2. Macro-hairs variable on the leaf margins………………………..scrobiculatum<br />
2. Macro-hairs constant on the leaf margins…………………….........conjugatum<br />
3. Papillae present on adaxial surfaces…………………………………………...4<br />
3. Papillae absent on both surfaces……………………………………………….2<br />
4. Micro-hairs present on both surfaces…………………………………………..2<br />
4. Micro-hairs absent on both surfaces………………………………....vaginatum<br />
Key to the three species studies based on their morphological features<br />
Inflorescence: Consisting <strong>of</strong> 2 long slender raceme between 8-15cm that has greenish yellow<br />
spikelets which are almost circular lying flat with hairy fringe on their margin……..P. conjugatum<br />
Inflorescence: Consisting <strong>of</strong> 2-10 racemes, each with two rows <strong>of</strong> overlapping swollen circular<br />
spikelets…...................................................................................................................P. scrobiculatum<br />
Leaves: Borne in two distinct ranks on either side <strong>of</strong> the culm<br />
Inflorescence: Consisting <strong>of</strong> 1-3 racemes, sometimes a pair <strong>of</strong> terminal racemes with 2 rows <strong>of</strong> overlapping ovate<br />
spikelets …………………………………………………..……..P. vaginatum<br />
DISCUSSION<br />
36<br />
C<br />
IC<br />
SSc<br />
OPB<br />
SHC<br />
LNC
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
The morphological (vegetative) features observed showed that there were little or slight differences in the features <strong>of</strong><br />
the three species <strong>of</strong> Paspalum studied and this suggests their differences in species level as they exhibited different<br />
characters though some <strong>of</strong> the characters were quite identical.<br />
Some differences in type <strong>of</strong> stem and the inflorescence and spikelets (Table 1) were observed, although the heights<br />
were almost the same in the three species except for P.scrobiculatum which grows up to 100cm. The analysis <strong>of</strong> the<br />
morphological structure <strong>of</strong> the three studied species has revealed characteristics, which correspond to those<br />
mentioned by Lowe (1989) and Akobundu and Agwayaka (1998). The epidermal cells are arranged in horizontal<br />
files. Leaf epidermis <strong>of</strong> the genus Paspalum is clearly distinguished into coastal and intercoastal zones. The coastal<br />
zones are generally narrower while the intercoastal zones are broader. <strong>Studies</strong> carried out by Sharma and Salam<br />
(1984); Sharma and Mittal (1986) have reported similar observations in other genera and tribes <strong>of</strong> Poaceae. The<br />
epidermal cells possess sinuous, slightly to straight anticlinal walls. Metcalfe (1960) reported similar undulations in<br />
various genera and tribes <strong>of</strong> Poaceae. Explanations have been given for the wavy nature <strong>of</strong> the anticlinal walls <strong>of</strong> the<br />
epidermal cells. One <strong>of</strong> the explanations for this phenomenon relates the undulations to the development <strong>of</strong> stress<br />
during the differentiation <strong>of</strong> the leaf (Avery, 1933). Another concept is that the waviness is caused by the method <strong>of</strong><br />
hardening <strong>of</strong> the differentiating cuticle (Watson, 1942). Furthermore, Linsbauer (1930) and Watson (1942) stated<br />
that the waviness is also affected by environmental conditions prevailing during leaf development. Prickles with<br />
hook shape have been observed in the adaxial and abaxial surfaces <strong>of</strong> P. conjugatum and P. scrobiculatum. Prickles<br />
with angular spines were restricted to the margins <strong>of</strong> leaf lamina <strong>of</strong> the three species., various shapes <strong>of</strong> prickles in<br />
tribes <strong>of</strong> Poaceae have been described by Sharma and Mittal (1986) Sharma and Salam (1984). Font Quer (1975)<br />
defines papillae as the simplest <strong>of</strong> trichomes, characterized by wall projection followed by the protoplast <strong>of</strong><br />
epidermal cells. According to Ellis (1979), Poaceae papillae occur in long and short cells, especially in intercostal<br />
zones, in numbers that may vary from one to many per cell. Papillae are absent in most <strong>of</strong> the three species studied<br />
except on the adaxial surface <strong>of</strong> P. vaginatum where it was found to be present. Thus, the absence <strong>of</strong> papillae in this<br />
last mentioned species can be interpreted as a taxonomic indicator. Micro-hairs observed are mainly bi-cellular with<br />
tapering apices in the intercoastal zones <strong>of</strong> both the adaxial and abaxial surfaces <strong>of</strong> P. conjugatum and P.<br />
scrobiculatum. Metcalfe (1960) have described bi-cellular hairs in a number <strong>of</strong> grass species. Macro-hairs were<br />
absent in the coastal and intercoastal zones <strong>of</strong> the three species but were present on the margins <strong>of</strong> P. conjugatum. In<br />
P. scrobiculatum, it varied (i.e it was present in some and absent in the others). The reason for this could be<br />
probably due to the presence or absence <strong>of</strong> hairs on the leaf margins <strong>of</strong> the grass or other factors could be<br />
responsible. The stomata are restricted to the intercoastal zones on both adaxial and abaxial surfaces. According to<br />
Ellis (1979), the Poaceae stomata generally occur in well-defined bands in intercostal zones, and they may be<br />
classified according to the shape <strong>of</strong> subsidiary cells. Subsidiary cells <strong>of</strong> the stomata varied from triangular to low<br />
dome shape in the adaxial surface <strong>of</strong> P. conjugatum while it was the same in the abaxial surfaces <strong>of</strong> the remaining<br />
two species. Mensah and Gill (1997) have reported similar observations in other genera and tribes <strong>of</strong> Poaceae like<br />
Sporoboleae. Opaline bodies which are depositions <strong>of</strong> silica materials were mainly dumbbell, cross, saddle and<br />
horizontally elongated in shape. The importance <strong>of</strong> opaline bodies as a systematic tool in grasses has been<br />
overemphasized by many researchers including Metcalfe (1960).<br />
Grasses are currently identified based on their floral characters, but a problem encountered with the system <strong>of</strong><br />
identification is that grasses do not flower for a greater part <strong>of</strong> their life cycle. Hence, a biosystematic approach<br />
could be used in tackling this problem through gathering <strong>of</strong> data from various studies such as cytology, palynology,<br />
epidemiology etc. The study <strong>of</strong> different epidermal characters such as macro-hairs, prickles, papillae, micro-hairs,<br />
distribution <strong>of</strong> stomata, nature <strong>of</strong> long cells, subsidiary cells, opaline bodies and surface views <strong>of</strong> the leaf helps us<br />
classify and identify grasses into their various tribes and genus and thus adds to our knowledge on the<br />
biosystematics <strong>of</strong> grass species. It will also be beneficial as a research tool to cytologist, weed scientist and research<br />
workers.<br />
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Ellis R. P. (1979). A procedure for standardizing comparative leaf anatomy in the Poaceae II: the epidermis as seen<br />
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Euphytica 104: 119-125<br />
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from West Africa. J.Plant.Anat.Morph.7: 72-81.<br />
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38
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Digital Moulding <strong>of</strong> the Solicitations within the Dielectric <strong>of</strong><br />
the Transformers and the Evaluation <strong>of</strong><br />
Life Cycle <strong>of</strong> the Insulation Systems<br />
MARIUS-CONSTANTIN POPESCU* and CRISTINEL POPESCU<br />
Faculty <strong>of</strong> Electromechanical and Environmental Engineering, University <strong>of</strong> Craiova,<br />
B-dul Decebal, nr.107, 200440-Craiova, Dolj, ROMÂNIA<br />
*E-mail address for correspondence: mrpopescu@em.ucv.ro<br />
_________________________________________________________________________________________<br />
Abstract: This papers analyses the evaluation methods <strong>of</strong> the wear <strong>of</strong> transformers that occurs on their charging<br />
with alternating load, taking into consideration mainly the thermal ageing <strong>of</strong> electroinsulation material,<br />
especially <strong>of</strong> those <strong>of</strong> A class.<br />
Key-Words: wear <strong>of</strong> transformer, thermal parameters.<br />
_________________________________________________________________________________________<br />
INTRODUCTION<br />
In regular service conditions, the transformer is subject to added solicitations which influence the long-term<br />
response <strong>of</strong> the transformer. Among the elements <strong>of</strong> the transformer, the insulation, which this chapter deals<br />
with, is stressed in different conditions in use from those <strong>of</strong> the lab. In regular service conditions the insulation <strong>of</strong><br />
the transformers is under nominal voltage <strong>of</strong> the electric network, reaching the crest working voltage at the most.<br />
In lab conditions, the insulation <strong>of</strong> the transformers is subject to the action <strong>of</strong> pro<strong>of</strong> stress which has the value,<br />
form and time period appropriate for the concepts and actual conditions <strong>of</strong> coordination <strong>of</strong> the insulation, applied<br />
in transformer plants and distribution stations. As a result, the testing <strong>of</strong> the insulation <strong>of</strong> the transformers in lab<br />
must guarantee the safe running <strong>of</strong> the transformers under most unfavorable conditions. The insulation <strong>of</strong> the<br />
electrical power transformers is subject to different kinds <strong>of</strong> stress, both in real and in lab conditions. In standard<br />
conditions, electrical (<strong>of</strong> nominal voltage and <strong>of</strong> overvoltage), mechanical (due to the short-circuit stresses),<br />
chemical (due to deposits or chemical agents) and thermal (due to changes in temperature and in the atmosphere)<br />
stresses are applied on the insulation. Due to these stresses, in the course <strong>of</strong> utilization, the properties <strong>of</strong> the<br />
electroinsulation materials deteriorate, bringing about the ageing <strong>of</strong> these materials. On the whole, the ageing<br />
process <strong>of</strong> the insulating materials is a complex process because <strong>of</strong> the multitude <strong>of</strong> different kinds <strong>of</strong> factors<br />
which influence it. Among these stresses, those which influence the most the insulation are those due to internal<br />
overvoltage, caused by the changes in the parameters <strong>of</strong> the electroenergetic system, and to external overvoltage<br />
(atmospherical), caused by lightning, the temperature <strong>of</strong> the oil/paper insulation complex from the transformer<br />
respectively. After the changes in the physical properties <strong>of</strong> the electroinsulation materials, changes occurred in<br />
use, the marking <strong>of</strong> the state <strong>of</strong> an insulation can not be carried out taking into consideration a single property<br />
due to the fact that the changes are the result <strong>of</strong> the action <strong>of</strong> a large number <strong>of</strong> external actions, the<br />
combinations <strong>of</strong> which are random, their accurate reproduction being impossible. It is difficult to study the<br />
transformers while they are working, because it would take a long time, namely decades. Shortening the length<br />
<strong>of</strong> the trials could be carried out by introducing accelerated ageing procedures, but these methods do not<br />
guarantee results that can be applied in real conditions. Therefore, the trial conditions must be created in a way<br />
that they are as similar as possible to the real ones and in accordance to the purpose for which the results are<br />
used later on. For this reason, the functional trials carried out on mock-ups are <strong>of</strong> great scientific value.<br />
39
1.External stresses <strong>of</strong> the insulation <strong>of</strong> the electrical power transformers<br />
In the case <strong>of</strong> the external stresses, the potential pulse that applies stresses on the insulation can be:<br />
- full-wave impulse - <strong>of</strong> long standing, after which high voltage oscillations develop in the windings hence<br />
resulting stresses both among the spires and between the winding and the earth point.<br />
- chopped-wave impulse – the amplitude <strong>of</strong> which is not so great, but due to scarp cutting, it can bring about<br />
voltage gradients that are dangerous to the insulation on entrance or at the neutral point <strong>of</strong> the transformer.<br />
- steep-wave impulse – has great amplitude but it lasts little and as a consequence it produces the most stresses.<br />
These can apply stress on the insulation at the table and the insulation among the entrance spires <strong>of</strong> the winding.<br />
In lab conditions, the transformer is subject to a minute sinusoidal pro<strong>of</strong> voltage, namely a pro<strong>of</strong> voltage <strong>of</strong><br />
impulse. Each <strong>of</strong> the pro<strong>of</strong> voltages is referred to maximum overvoltage in use, equating the overvoltage in use<br />
to lab conditions.<br />
The pro<strong>of</strong> voltage <strong>of</strong> the internal insulation with full-wave is stated by the relation:<br />
[Uinc]up=Kt[Ugp]up+0,5UN (1)<br />
where: Kt is coefficient with the value 1.15 for the 6 -35 kV transformers and 1.10 for the 110 and 220 kV<br />
transformers; UN is nominal voltage <strong>of</strong> the winding <strong>of</strong> the transformer.<br />
The pro<strong>of</strong> voltage <strong>of</strong> the internal insulation with the chopped-wave impulse is stated by the relation:<br />
[Uinc]ut=1.15*1.25[Ugp]up (2)<br />
where 1.15 takes into account the cumulative effect, and 1.25 takes into account the increase <strong>of</strong> voltage at the lug<br />
<strong>of</strong> the transformer in relation with the lightning arrester.<br />
The minute sinusoidal pro<strong>of</strong> voltage is stated by the relation:<br />
�U �<br />
inc �<br />
Ua�<br />
�<br />
� � K<br />
si<br />
c<br />
where: βsi is equation coefficient <strong>of</strong> the Usi internal overvoltages in use with the Uα minute pro<strong>of</strong> voltages in lab;<br />
Kc ≈0.9 is the coefficient that takes into account the cumulative effect <strong>of</strong> repeated stresses in exploitation.<br />
2. Factors that determine the state <strong>of</strong> the insulation<br />
The insulation <strong>of</strong> the transformers is influenced by the following factors [1, 2, 4, 5]:<br />
The alien substances in the internal insulation are: moisture left in the insulation after an inappropriate drying<br />
procedure; residues <strong>of</strong> the coating varnish solvent that have not been removed when the windings were dried;<br />
blisters or gaseous inclusions left in the insulation after the filling <strong>of</strong> the transformer with oil; dirt resulted from<br />
an inappropriate operating process. The contamination <strong>of</strong> the external insulation, the thermal operating<br />
conditions and the altitude at which the transformer works. Damping the insulation causes: an increase in<br />
dielectric losses and a decrease in dielectric rigidity. The presence in oil <strong>of</strong> water in the form <strong>of</strong> emulsion (in<br />
dispersed state) leads to a rapid decrease <strong>of</strong> rupturing voltage <strong>of</strong> the oil. The water molecularly dissolved in oil<br />
does not influence the dielectric rigidity and losses. But in the presence <strong>of</strong> alien fields in the oil-water<br />
molecularly dissolved changes into dispersed state leading to the decrease <strong>of</strong> dielectric rigidity. Variations in<br />
temperature also cause changes in rupturing voltage. Thus, when the temperature increases from 20�C to 60�C,<br />
at a frequency <strong>of</strong> 50 Hz, an important increase in rupturing voltage takes place. The electrical insulating oil,<br />
commercially pure, contains an amount <strong>of</strong> moisture, dissolved gases and solid impurities (waste and grains).<br />
When the temperature increases the dilution <strong>of</strong> water increases and the waters turns from the state <strong>of</strong> emulsion<br />
into the state <strong>of</strong> dilution leading to the decrease <strong>of</strong> dielectric rigidity. The effect that the temperature variations<br />
40<br />
(3)
have on the insulation <strong>of</strong> the transformers in a long time cause an ageing <strong>of</strong> the insulation, which loses its<br />
mechanical properties (it becomes fragile). The impurities and the dirt from the atmosphere reduce the value <strong>of</strong><br />
the rupturing voltage <strong>of</strong> the external insulation <strong>of</strong> the transformers, even under working stress. Gaseous<br />
inclusions or blisters lead to partial discharges and thus to the decomposition <strong>of</strong> the structural insulation, having<br />
negative effects on the dielectric rigidity as it decreases. Low atmospheric pressure in mountainous regions cause<br />
the decrease <strong>of</strong> the voltage <strong>of</strong> the external insulation because <strong>of</strong> the decrease <strong>of</strong> the relative density <strong>of</strong> the air.<br />
The quality <strong>of</strong> the impregnation process and especially the polymerization degree <strong>of</strong> the varnish highly influence<br />
the condition <strong>of</strong> the insulation <strong>of</strong> the transformers, incomplete polymerization causing an increase in dielectric<br />
losses, the decrease <strong>of</strong> the dielectric rigidity, the oxidation and ageing <strong>of</strong> the electrical insulating oil.<br />
3. The testing <strong>of</strong> the insulation <strong>of</strong> transformers<br />
The testing with direct voltage have as purpose the finding out <strong>of</strong> the dampness <strong>of</strong> the insulation <strong>of</strong> transformers,<br />
if there are or not deficiencies able to cause partial discharges (gaseous inclusions, deficient junctions), if<br />
changes in the response <strong>of</strong> the dielectric occur by applying stress for a long period <strong>of</strong> time. Based on the<br />
variations from the initial state <strong>of</strong> the insulation, variations caused by the influence <strong>of</strong> dampness, <strong>of</strong> the ageing <strong>of</strong><br />
the insulation <strong>of</strong> the transformers or <strong>of</strong> an overcharge, it can be decided if the occurring deficiencies can be<br />
remedied or if the transformer must be submitted to a general overhaul. Furthermore, the main tests on the<br />
electrical power transformers are presented [4], [7], [10], [12], [14], [15], [16].<br />
The measurement <strong>of</strong> the insulation resistance. The insulation resistance, through the absorption coefficient<br />
R60/R15 allows the estimation <strong>of</strong> the degree <strong>of</strong> moistness <strong>of</strong> the insulation <strong>of</strong> transformers. For a dry enough<br />
transformer the absorption coefficient must relate to the following: R60/R15≥1,5. When applying direct voltage,<br />
in time, an alternative current is established through the dielectric which decreases and then settles at a value.<br />
Initially the current has a high value and thus the insulation resistance has a high value due to the polarization<br />
current and to the charging current. Compared to a dry dielectric, at a damp dielectric, to the polarization current,<br />
displacement current, an orientation component is added and as a consequence the line current rises. The<br />
insulation resistance <strong>of</strong> a dielectric is given by the relation between the applied direct voltage and the resulted<br />
full current. The value <strong>of</strong> the insulation resistance is influenced by the following factors: the value <strong>of</strong> the direct<br />
voltage which is applied, the length <strong>of</strong> applying the voltage, the electrostatic charge, the temperature <strong>of</strong> the<br />
insulation and the dampness degree <strong>of</strong> the insulation. The state <strong>of</strong> the insulation <strong>of</strong> the transformer is determined<br />
through the diagram I=f(U) by means <strong>of</strong> the position <strong>of</strong> the break which appears in the curve at a certain value <strong>of</strong><br />
the voltage. The higher the voltage at which the break appears and the gentler the transfer from a slope to another<br />
is, the better the state <strong>of</strong> the insulation is. If the break appears below the value 2 * U max,<br />
the insulation is<br />
considered to be weakened and the transformer must be overhauled. If the current suddenly increases the<br />
insulation is disrupted and the tests must be stopped. The state <strong>of</strong> the insulation <strong>of</strong> the transformer can also be<br />
determined through the variation <strong>of</strong> the insulation resistance and <strong>of</strong> the current depending on the applied voltage.<br />
After a while the insulation resistance, namely the through the insulation reach a set value. If the stabilization<br />
takes place in a short period <strong>of</strong> time and also at a low value, it means that the conductance component IS is high<br />
compared to the polarization component Ip and consequently the insulation is damp. On the other hand, the low<br />
values <strong>of</strong> the insulation resistance due to the high content <strong>of</strong> water in the insulation do not mean that the<br />
transformer is aged or permanently deteriorated. The insulation resistance is not standardized. It is to be<br />
compared with the values <strong>of</strong> the measurements at the same temperature. If the previous measurements have been<br />
carried out at different temperatures then their values are reduced to the temperature <strong>of</strong> the latest measurement.<br />
The insulation resistance varies in inverse ratio to the temperature. As the measurements can not be carried out<br />
all the time at the same temperature, recomputed values are used, recomputed through recomputation values <strong>of</strong><br />
the insulation resistance depending on the temperature. For each transformer two measurements are carried out<br />
at temperatures between 20�C and 75�C. The relation to the same temperature is performed by the multiplication<br />
or the division <strong>of</strong> the values <strong>of</strong> the insulation resistance with its variation coefficient by the temperature<br />
difference K1 following the values presented in Table 1.<br />
Δt<br />
( 0 C)<br />
Table 1. The values <strong>of</strong> the coefficient <strong>of</strong> variation K1<br />
1 2 3 4 5 10 15 20 25 30 35 40 45 50<br />
Val K1 1.05 1.07 1.12 1.16 1.23 1.4 1.74 2.23 2.65 3.35 4.05 5.15 6,1 7.5<br />
41
The insulation resistance must not drop below 70% <strong>of</strong> the initial value <strong>of</strong> the insulation resistance. When<br />
measuring, the following are taken into consideration:<br />
- For the new transformers, when putting it to service, the R60 value must not be below 70% <strong>of</strong> the its value set in<br />
the factory;<br />
- For the transformers in use, R60 must not drop below the values shown in Table 2.<br />
Un (kV)<br />
Table 2. R60 values for different values <strong>of</strong> the nominal voltage.<br />
R60<br />
20 0 C 50 0 C<br />
≤ 60 300 90<br />
110 – 220 600 180<br />
400 1000 300<br />
In time, the insulation resistance <strong>of</strong> the transformer rises up to practically a set value. The variation <strong>of</strong> the<br />
insulation resistance in relation with the time represents the absorption curve. The measurement <strong>of</strong> the insulation<br />
resistance is carried out after 15, 60s respectively. The absorption coefficient R60/R15 tends to the value 1if the<br />
insulation has a great content <strong>of</strong> dampness. The absorption coefficient provides information on the variation <strong>of</strong><br />
the insulation resistance in time, which is why the state <strong>of</strong> the insulation resistance is judged by absorption<br />
curves and polarization curves. The absorption coefficient is used as one <strong>of</strong> the criteria to establish the dampness<br />
<strong>of</strong> the curves, the shape <strong>of</strong> the absorption curve depending on the degree <strong>of</strong> dampness <strong>of</strong> the dielectric and its<br />
build. The absorption curve shows the variation <strong>of</strong> the insulation resistance in time and <strong>of</strong> the current through the<br />
insulation. The measurements are carried out in the specified thermal and dampness conditions, in fair weather,<br />
at a relative dampness <strong>of</strong> the environment, <strong>of</strong> 80% at the most, taking into consideration the following<br />
observations:<br />
- When it starts working the Kabs value must not be over 5% below the value set in the factory;<br />
- For the transformers in use the Kabs value is not standardized;<br />
- The value <strong>of</strong> the absorption coefficient at 20�C is considered normal if: Kabs≥1,2 for power transformers with<br />
U≤110kV; Kabs≥1,3 for power transformers with U≤110kV.<br />
The dissipation factor. The tgδ dissipation factor is also a criterion for evaluating the state <strong>of</strong> the insulation. The<br />
increase <strong>of</strong> the tgδ value is determined by the chemical degradation <strong>of</strong> the oil, its getting wet, the ageing <strong>of</strong> the<br />
solid insulation affected by dampness, oxigen or by temperature. The measuring <strong>of</strong> tgδ is compulsory for all<br />
transformers <strong>of</strong> over 110kV voltage and powers <strong>of</strong> over 10 MVA inclusive, respecting the following<br />
observations:<br />
- When putting into service tgδ the measuring must be carried out at the temperature recommended in the manual<br />
provided by the factory (±5 0 C), not below 10 0 C .<br />
- The values measured at the putting into function are compared to the values measured in the factory. The<br />
values in use must be kept between the limits provided in the Table 3.<br />
Table 3. Normal values for tgδ.<br />
Un (kV) 20 0 C 50 0 C<br />
In use, the values obtained for tgδ at one <strong>of</strong> the two reference temperatures is compared to the values measured<br />
previously (in the factory, at putting into service). In the case <strong>of</strong> new transformers, the tgδ value must not<br />
increase over the value set in factory with over 30%. If the previous measurement has been carried out at a<br />
different temperature from the one <strong>of</strong> the latest measurement, it will relate to the temperature <strong>of</strong> the latest<br />
measurement by division or multiplication by the coefficient <strong>of</strong> variation K2, depending on the difference <strong>of</strong><br />
temperature Δt ( 0 C).<br />
Δt<br />
( 0 C)<br />
Table 4. The values <strong>of</strong> the coefficient K2<br />
1 2 3 4 5 10 15 20 25 30 35 40 45 50 55 60<br />
Val K2 1.04 1.07 1.10 1.11 1.16 1.26 1.52 1.65 2 2.4 2.55 3 3.4 4 4.5 5.4<br />
For all transformers, the real values <strong>of</strong> the reporting coefficient is determined from the diagram obtained from<br />
measuring the tgδ at the temperature <strong>of</strong> 50±5 0 C, after which the tgδ=f(t) line is used when the temperature has<br />
dropped to 20±5 0 C. For measuring we employ a measuring bridge for MD – 16 capacity assembled after a<br />
Scherine assemblage.<br />
The measuring <strong>of</strong> the ohmic resistance <strong>of</strong> the curves. The purpose <strong>of</strong> the measuring <strong>of</strong> the ohmic resistance <strong>of</strong><br />
the curves is: to determine the real resistance <strong>of</strong> the curves; to check the welds or junctions from the conductors<br />
<strong>of</strong> the windings; to track down the possible interruptions; to make evident the dead short circuits among the<br />
spires or other deficiencies which are reflected in the value <strong>of</strong> the resistance. The measuring is carried out in<br />
direct current at a value that exceeds with 20% the value <strong>of</strong> the non-load current, but it is not to exceed 0,1In.<br />
While the ohmic measurements are carried out, the winding temperature is put down. The measured resistance is<br />
related to another temperature by means <strong>of</strong> the relation:<br />
T � t<br />
R * 2<br />
t � R<br />
2 t1<br />
T � t1<br />
T = 235 both for the copper windings and for the aluminum windings.<br />
Taking these into consideration, some special measurements have been carried out on some electrical power<br />
transformers from Romania. The gathered data, recorded in the task report, have been synthesized in a tabular<br />
and graphic form. Analyzing the result <strong>of</strong> the measurements, conclusions regarding the behaviour <strong>of</strong> the<br />
transformers in use could be drawn. Fig’s 1 and 2 show the results <strong>of</strong> the measurements carried out on electrical<br />
power transformers considered to be matters <strong>of</strong> study. The study has been completed for the main sizes that<br />
characterize the behavior <strong>of</strong> the transformers, from 1998 to 2008. For each size the measured value has been<br />
compared to the normalized value and to the value EPC set in the factory. From the obtained data and the<br />
graphical representations it can be determined that only in the case <strong>of</strong> the transformer T11 (from a Station in<br />
Romania) a negative variation can be observed both <strong>of</strong> the insulation resistance and <strong>of</strong> the tangent delta,<br />
especially between 2004 and 2005. As a consequence, the increase <strong>of</strong> the insulation over the EPC values calls for<br />
a further close surveillance <strong>of</strong> the insulation. The rest <strong>of</strong> the transformers can be considered suitable to be in<br />
service.<br />
Table 5. The result <strong>of</strong> the measurements TS – earth point performed on the T9 power transformer.<br />
EPC<br />
Tg la EPC 38 C<br />
Tg EPC trans la 20C<br />
R 15 EPC la 38 1200 TS-TI Trafo 11<br />
R 15 EPCla 20 2472<br />
R 60 EPCla 38 2400 Vn 20 C= 600 Mohm Vn 50 C=180 Mohm<br />
R 60 EPCla 20 4944 Vn 20 C= 2,5% Vn 50 C= 7 %<br />
R1-rez EPCla 38 1,373 An EPC-1986<br />
t1-EPC 38 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005<br />
Tg mas trans la 20 C 0,23 0,25 0,29 0,28 0,32 0,24 0,28 0,25 0,25 0,23 0,30<br />
Tg masurata 0,35 0,38 0,4 0,42 0,45 0,4 0,42 0,4 0,38 0,4 0,42<br />
%R60mas din R60EPC la 20gr 60 65 51 49 54 60 49 50 41 56 54<br />
R60 transpus la 20 2980 3220 2527 2429 2652 2966 2429 2448 2024 2768 2652<br />
R 60 masurata 1560 1750 1560 1320 1560 1440 1320 1230 1100 1230 1560<br />
Roh plot 1-mas 1,332 1,326 1,312 1,325 1,313 1,345 1,326 1,338 1,325 1,353 1,316<br />
t2-calc la mas 38,0 36,5 35,4 32,9 35,3 33,1 38,9 35,4 37,6 35,3 40,4 33,6<br />
Delta t<br />
kiz<br />
18,0<br />
2,06<br />
16,5<br />
1,91<br />
15,4<br />
1,84<br />
12,9<br />
1,62<br />
15,3<br />
43 1,84<br />
13,1<br />
1,7<br />
18,9<br />
2,06<br />
15,4<br />
1,84<br />
17,6<br />
1,99<br />
15,3<br />
1,84<br />
20,4<br />
2,25<br />
13,6<br />
1,7<br />
k tg 1,65 1,55 1,51 1,38 1,51 1,42 1,65 1,51 1,6 1,51 1,75 1,42<br />
R15 transpus la 20 2197 1748 1426 1838 1105 1813 1041 1325 1593 1766 1586<br />
R15 masurat 1150 950 880 999 650 880 566 666 866 785 933<br />
Kabs 1,36 1,84 1,77 1,32 2,40 1,64 2,33 1,85 1,27 1,57 1,67<br />
(4)
Fig. 1. The variation <strong>of</strong> the insulation resistance <strong>of</strong> the T9 power transformer.<br />
Table 6. The TS – TI measurement results performed on the T 11 power transformer.<br />
EPC<br />
Tg la EPC 38 C 0,49<br />
Tg EPC trans la 20C 0,30<br />
R 15 EPC la 38 2680 TS-masa Trafo 9 st Mare - 199999<br />
R 15 EPCla 20 5521<br />
R 60 EPCla 38 4930 Vn 20 C= 600 Mohm Vn 50 C=180 Mohm<br />
R 60 EPCla 20 10156 Vn 20 C= 2,5% Vn 50 C= 7 %<br />
R1-rez EPCla 38 1,353 An EPC-1986<br />
t1-EPC 38 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006<br />
Tg mas trans la 20 C 0,29 0,25 0,25 0,26 0,30 0,30 0,32 0,28 0,32 0,29 0,32 0,31<br />
Tg masurata 0,45 0,38 0,35 0,4 0,43 0,5 0,48 0,45 0,48 0,5 0,45 0,45<br />
%R60mas din R60EPC la 20gr 33 31 27 27 26 27 26 29 29 32 32 31<br />
R60 transpus la 20 3343 3110 2722 2760 2635 2719 2668 2985 2944 3263 3230 3186<br />
R 60 masurata 1750 1690 1680 1500 1550 1320 1450 1500 1600 1450 1900 1800<br />
Roh plot 1-mas 1,332 1,326 1,312 1,325 1,313 1,345 1,326 1,338 1,325 1,353 1,316 1,322<br />
t2-calc la mas 38,0 36,5 35,4 32,9 35,3 33,1 38,9 35,4 37,6 35,3 40,4 33,6 34,7<br />
Delta t 18,0 16,5 15,4 12,9 15,3 13,1 18,9 15,4 17,6 15,3 20,4 13,6 14,71377<br />
kiz 2,06 1,91 1,84 1,62 1,84 1,7 2,06 1,84 1,99 1,84 2,25 1,7 1,77<br />
k tg 1,65 1,55 1,51 1,38 1,51 1,42 1,65 1,51 1,6 1,51 1,75 1,42 1,46<br />
R15 transpus la 20 3362 3533 1944 2429 1870 3296 3165 3343 2263 2768 2584 2620<br />
R15 masurat 1760 1920 1200 1320 1100 1600 1720 1680 1230 1230 1520 1480<br />
Kabs 0,99 0,88 1,40 1,14 1,41 0,83 0,84 0,89 1,30 1,18 1,25 0,00<br />
Fig. 2. The variation <strong>of</strong> the dissipation factor <strong>of</strong> the T9 power transformer.<br />
Fig. 3. The variation <strong>of</strong> the insulation resistance <strong>of</strong> the T 11 power transformer.<br />
44
Fig. 4. The variation <strong>of</strong> tangent delta <strong>of</strong> the T11 power transformer.<br />
Table 7. The results <strong>of</strong> the TI – earth point measurements performed on the T11 power transformer.<br />
EPC<br />
Tg la EPC 38 C 0,25<br />
Trafo 11<br />
Tg EPC trans la 20C 0,15<br />
R 15 EPC la 38 1000 TI-masa<br />
R 15 EPCla 20 2060<br />
R 60 EPCla 38 2200<br />
Vn 20 C= 600 Mohm Vn 50 C=180 Mohm<br />
R 60 EPCla 20 4532<br />
Vn 20 C= 2,5% Vn 50 C= 7 %<br />
R1-rez EPCla 38 1,373 An EPC-1986<br />
t1-EPC 44 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005<br />
Tg mas trans la 20 C 0,21 0,24 0,30 0,34 0,44 0,44 0,33 0,21 0,29 0,31 0,37<br />
Tg masurata 0,33 0,36 0,42 0,52 0,62 0,72 0,5 0,33 0,44 0,55 0,52<br />
%R60mas din R60EPC la 20gr 70 63 58 67 64 78 71 76 69 79 65<br />
R60 transpus la 20 3171 2852 2608 3036 2890 3543 3220 3423 3128 3600 2924<br />
R 60 masurata 1660 1550 1610 1650 1700 1720 1750 1720 1700 1600 1720<br />
Roh plot 1-mas 1,332 1,326 1,312 1,325 1,313 1,345 1,326 1,338 1,325 1,353 1,316<br />
t2-calc la mas 38,0 36,5 35,4 32,9 35,3 33,1 38,9 35,4 37,6 35,3 40,4 33,6<br />
Delta t 18,0 16,5 15,4 12,9 15,3 13,1 18,9 15,4 17,6 15,3 20,4 13,6<br />
kiz 2,06 1,91 1,84 1,62 1,84 1,7 2,06 1,84 1,99 1,84 2,25 1,7<br />
k tg 1,65 1,55 1,51 1,38 1,51 1,42 1,65 1,51 1,6 1,51 1,75 1,42<br />
R15 transpus la 20 1815 1693 2138 1582 1105 3193 2453 3483 1380 1575 1326<br />
R15 masurat 950 920 1320 860 650 1550 1333 1750 750 700 780<br />
Kabs 1,75 1,68 1,22 1,92 2,62 1,11 1,31 0,98 2,27 2,29 2,21<br />
Fig. 5. The variation <strong>of</strong> the insulation resistance <strong>of</strong> the T11 power transformer.<br />
45
Fig. 6. The variation <strong>of</strong> the dissipation factor <strong>of</strong> the T11 power transformer.<br />
4.Thermal ageing <strong>of</strong> the electroinsulation materials<br />
The lifetime <strong>of</strong> a transformer is influenced by a series <strong>of</strong> factors which determine the changes in physical<br />
properties, properties <strong>of</strong> a mechanical, electrical, thermal or chemical nature.<br />
- Alien substances in the internal insulation: moisture left in the insulation after an inappropriate drying<br />
procedure; residues <strong>of</strong> the coating varnish solvent that have not been removed when the windings were dried;<br />
blisters or gaseous inclusions left in the insulation after the filling <strong>of</strong> the transformer with oil; dirt resulted from<br />
an inappropriate operating process. The damping <strong>of</strong> the insulation brings about an increase <strong>of</strong> the dielectric<br />
losses as well as a decrease <strong>of</strong> the dielectric rigidity.<br />
- The contamination <strong>of</strong> the external insulation, the thermal operating conditions and the altitude at which the<br />
transformer works.<br />
The ageing <strong>of</strong> the transformers occurs due to the alterations <strong>of</strong> the physical properties, ageing that brings about<br />
the reduction <strong>of</strong> their lifetime. The way in which the external factors influence the transformers' lifetime is hard<br />
to study as such a study includes some pro<strong>of</strong> tests that take a great deal <strong>of</strong> time, that is decades. This is why the<br />
study time must be reduced by reducing the period <strong>of</strong> testing and by settling the conditions <strong>of</strong> the testings. For<br />
this purpose functional testings on models are employed. Consequently, mathematical laws have been<br />
established to mirror as much as possible the ageing process <strong>of</strong> the transformers.<br />
Concerning the electrical equipment, the most sensitive component is the insulation, the lifetime <strong>of</strong> which<br />
actually determines the lifetime <strong>of</strong> the equipment. Concerning electrical transformers and static devices<br />
generally, the ageing <strong>of</strong> the insulation is essential. For the lifetime, laws have been defined experimentally to<br />
state the lifetime <strong>of</strong> the insulation. For example the Montsinger’s law in which the lifetime is expressed in<br />
degrees Celsius, while in Bűssing’s law the lifetime is expressed in degrees Kelvin.<br />
���<br />
D � �*<br />
e , (5)<br />
V. M. Montsinger’s relation, valid for temperatures between 90� C and 110� C, namely<br />
B<br />
T<br />
D � A*<br />
e , (6)<br />
W. Bűssing’s relation, valid for a large range <strong>of</strong> temperatures and for a great number <strong>of</strong> materials <strong>of</strong> different<br />
classes, here: D - the lifetime <strong>of</strong> electroinsulant materials; θ, T – the temperature <strong>of</strong> the electroinsulant material<br />
expressed in degrees Celsius, in degrees Kelvin respectively; α, β, A, B – constant specific to the electroinsulant<br />
material.<br />
The ageing method is based on Arhhenius’s equation, which expresses the degradation rate <strong>of</strong> an electroinsulant<br />
material:<br />
46
�E<br />
�<br />
� � A*<br />
e KT<br />
, (7)<br />
Arhhenius’s relation, where: A is constant specific to the material; ΔE is activation energy; K is Boltzman’s<br />
constant; T is the temperature <strong>of</strong> the electroinsulant material expressed in degrees Kelvin.<br />
The law expressed by the relation (5) was established by V.M. Montsinger and it was proved to be valid for A<br />
class electroinsulant materials, but for a relatively limited range <strong>of</strong> temperature, 90�C...110�C. The law given by<br />
the relation (6) was demonstrated for the first time by W. Bűssing through the kinetic theory <strong>of</strong> chemical<br />
reactions and it proved to be valid for a great deal <strong>of</strong> electroinsulant materials <strong>of</strong> different classes and for a wide<br />
range <strong>of</strong> temperatures. The lifetime laws <strong>of</strong> electroinsulant materials take into account not only the temperature<br />
as decisive factor, but also the other factors. The other factors are taken into account when choosing the<br />
constants A and B, and α and β. The values <strong>of</strong> these constants are chosen in keeping with functional trials <strong>of</strong><br />
accelerated ageing. The factors which determine the ageing <strong>of</strong> the transformers determine their lifetime, deriving<br />
from the lifetime equation <strong>of</strong> transformers. Thus, the ageing <strong>of</strong> transformers is marked by:<br />
- The relative factor <strong>of</strong> thermal ageing, also named relative factor <strong>of</strong> thermal wear<br />
- Relative thermal ageing, also named relative thermal wear.<br />
The relative factor <strong>of</strong> thermal ageing is defined by:<br />
� B B �<br />
� � �<br />
�TN<br />
T � � � e<br />
(8)<br />
where: T is the absolute temperature expressed in degrees Kelvin; TN is the absolute temperature at which a<br />
normal lifetime if obtained; B is a constant characteristic to the material.<br />
Considering that the temperature varies in relation to time, the relative ageing factor will be, too, time function as<br />
follows:<br />
�(<br />
t) � e<br />
� B B<br />
� �<br />
�TN<br />
T<br />
The relative ageing factor p(t) marks the degradation rate <strong>of</strong> the insulating material and, thus, the extent <strong>of</strong> heat<br />
density <strong>of</strong> the electroinsulant material. Relative thermal ageing is given by the average value <strong>of</strong> the relative<br />
ageing factor in a certain period <strong>of</strong> time, namely:<br />
Replacing the expression for p(t), we obtain:<br />
1 �t<br />
u(<br />
t)<br />
�<br />
�t<br />
0<br />
47<br />
�<br />
� � � t �<br />
��(<br />
t)<br />
dt<br />
1<br />
u(<br />
t)<br />
� � e<br />
�t<br />
� B B �<br />
�t � � �<br />
�TN<br />
T ( t)<br />
�<br />
The two obtained expressions mark the thermal ageing <strong>of</strong> the electroinsulant material for a single time interval<br />
taken into consideration. If there are several time intervals taken into consideration, the expression <strong>of</strong> relative<br />
thermal ageing becomes:<br />
0<br />
(9)<br />
(10)<br />
(11)
n<br />
�ui�ti<br />
u(<br />
t)<br />
� i�1<br />
n<br />
(12)<br />
� �ti<br />
i�1<br />
Considering the same range <strong>of</strong> validity for the relations (5) and (6) written for the temperatures θ şi θN, and T şi<br />
TN, by equaling the following results:<br />
where the following can be written:<br />
and:<br />
e<br />
��<br />
( � ��<br />
)<br />
� �<br />
e<br />
N � e<br />
��(<br />
�N<br />
��)<br />
48<br />
B B<br />
�<br />
TN<br />
T<br />
1 �t<br />
����<br />
��<br />
�<br />
N ( t)<br />
u<br />
�<br />
� e dt<br />
�t<br />
0<br />
The two relations allow the evaluation <strong>of</strong> the ageing and wear degree <strong>of</strong> the insulation <strong>of</strong> electrical transformer.<br />
Where transformers are concerned, temperature is the main factor that influences their behavior, affecting<br />
especially the oil/paper insulation. In this case, dampness is another influencing factor, besides temperature. The<br />
ageing state marked by the thermal ageing factor p, the relative thermal ageing u, respectively, does not allow a<br />
different marking <strong>of</strong> the insulation considering temperature as main influencing factor. And that is because the<br />
degradation rate <strong>of</strong> the insulation is influenced by dampness at any temperature, and the ageing p factor may be<br />
considered as a ratio between two degradation rates, one <strong>of</strong> which the working temperature θ is expressed in<br />
degrees Celsius, namely T expressed in degrees Kelvin, the other at standard temperature θN, TN respectively, the<br />
relative ageing u being the average value <strong>of</strong> the ageing factor p in a certain period <strong>of</strong> time. thus, it may be<br />
considered that, if the change in the dampness degree influences in the same way the degradation rate <strong>of</strong> the<br />
oil/paper insulation, the ageing factor p can be regarded non dependent on dampness. The main component <strong>of</strong><br />
the ageing factor p is temperature, but at the same time, through the material constants α and β (actually θ şi β),<br />
A and B respectively (actually TN and B), it depends on the other chemical, mechanical or electrical factors that<br />
influence the ageing process <strong>of</strong> the oil/paper insulation from <strong>of</strong> the transformers.<br />
5.Thermal wear <strong>of</strong> the transformers<br />
In most cases the thermal wear <strong>of</strong> transformers in oil is determined by the wear <strong>of</strong> the paper impregnated with oil<br />
insulation. It is usually exposed to the highest <strong>of</strong> temperatures <strong>of</strong> the transformer close to the curves. The starting<br />
points <strong>of</strong> analyzing the wear <strong>of</strong> the transformer are two distinct cases: the temperature <strong>of</strong> the transformer varies<br />
distortionless with time and the temperature varies exponentially with time. Each <strong>of</strong> the cases can be treated as<br />
having as basis either Molntsinger’s law (5) or Bűssing’s law (6) [6], [9], [11], [14].<br />
6.1. The case <strong>of</strong> distortionless variation <strong>of</strong> temperature in relation with time<br />
The case in which the ageing <strong>of</strong> the transformer is reflected by Montsinger’s law (5). Taking into consideration<br />
at the initial moment t=0, θ=θi, after a time t=tf the temperature θ=θf respectively, the distortion less variation <strong>of</strong><br />
the temperature can be written in relation with time, in degrees Celsius, after an expression as follows:<br />
t<br />
� ( t) � �i<br />
� ��<br />
�t<br />
,<br />
��<br />
� �<br />
f � �i<br />
(13)<br />
(14)<br />
(15)<br />
(16)
where: θi is the temperature at the beginning <strong>of</strong> the time period taken into consideration, expressed in degrees<br />
Celsius; θf is the temperature at the end <strong>of</strong> the time period taken into consideration, expressed in degrees Celsius;<br />
Δt is the period <strong>of</strong> time during which the temperature increases from θi to θf.; t is time as current variable.<br />
The case in which the lifetime law <strong>of</strong> the transformer is expressed by the relation (6) given by Bűssing. In this<br />
case, the temperature variation in relation with time is expressed in degrees Kelvin after an expression as the<br />
following:<br />
T( t)<br />
� Ti<br />
� �T<br />
t<br />
�t<br />
There are the following relations between the two temperatures:<br />
,<br />
49<br />
T T � � �<br />
f i T<br />
(17)<br />
Ti=273+ θi; Tf=273+ θf, (18)<br />
namely ΔT=Δθ (19)<br />
The thermal ageing factor p as well as the relative thermal ageing u by means <strong>of</strong> their parameters link the relative<br />
sizes that lead to the ageing <strong>of</strong> the materials and based on the variation <strong>of</strong> these factors in time the curves that<br />
will characterise the ageing <strong>of</strong> the electroinsulant materials will be able to be marked <strong>of</strong>f. This paper deals with<br />
the evaluation <strong>of</strong> the relative thermal wear based on the Montsinger’s law employing the relation (5).<br />
Thus, considering the distortionless variation <strong>of</strong> temperature the relation becomes:<br />
By integrating the expression u(t), we bwill obtain:<br />
� � t ��<br />
�t ����N<br />
���i<br />
���*<br />
�<br />
1<br />
�<br />
t<br />
u t � e � � � �<br />
( ) � *<br />
�dt<br />
�t<br />
0<br />
1 � ��<br />
u � * e<br />
���<br />
��<br />
��N ��<br />
f � ��<br />
�<br />
�� ��<br />
e N i �� ��<br />
The expression (21) allows us to determine by computing the relative thermal wear, applicable both for a cooling<br />
process and in the case <strong>of</strong> one cooling process.<br />
6.2 The case <strong>of</strong> exponential variation <strong>of</strong> temperature in relation with time<br />
The exponential variation <strong>of</strong> temperature is deducted using the heating equation considering the parameter<br />
constant Tt only in input condition with P=constant. When I= constant, Tt depends on I, and when U=constant it<br />
depends on U and t. In these conditions we will continue to consider the hypothesis that P=constant and/or<br />
I=constant.<br />
In the case <strong>of</strong> exponential variation <strong>of</strong> temperature, temperatures θ and T become:<br />
respectively:<br />
t<br />
�<br />
T<br />
� �t� � �<br />
t<br />
r � ��*<br />
e<br />
(20)<br />
(21)<br />
(22)
T<br />
�t� � T � �T<br />
* e<br />
r<br />
where: θr, Tr – stand for stationary regime temperatures expressed in degrees Celsius, and degrees Kelvin<br />
respectively; Δθ, ΔT – stand for the difference between the stationary regime temperature and the temperature at<br />
the beginning <strong>of</strong> the thermal process expressed in degrees Celsius, and degrees Kelvin respectively; Tt is time<br />
constant with wich the temperature variation process takes place[s], having the following relation between the<br />
temperatures:<br />
50<br />
t T<br />
t<br />
�<br />
(23)<br />
Tr=273+ θr; Δθ=ΔT (24)<br />
The temperature differences Δθ, ΔT are <strong>of</strong> different symbols, according to the process, whether it is <strong>of</strong> cooling or<br />
<strong>of</strong> heating. If we take into consideration the thermal wear based on Montsinger’s relation, the following results:<br />
�t<br />
1<br />
u � � e<br />
�t<br />
0<br />
� � t ��<br />
� � � ��<br />
����<br />
���<br />
���<br />
T<br />
N<br />
��<br />
� �<br />
r * e t<br />
��<br />
� �<br />
�<br />
� �<br />
��<br />
�<br />
Placing the independent <strong>of</strong> time factors before the integral, the following results:<br />
��<br />
u �<br />
�� � � � �t<br />
N r<br />
�<br />
�t<br />
0<br />
e<br />
t<br />
�<br />
����*<br />
e<br />
Tt<br />
Consequently, the wear variation u can be figured for different values <strong>of</strong> the material constat β and certain values<br />
<strong>of</strong> the time value Tt.<br />
In order to simplify the display, relative values can be thus used:<br />
� � ��<br />
*<br />
;<br />
With the above, the expression <strong>of</strong> thermal wear becomes:<br />
e<br />
u �<br />
* t<br />
t �<br />
Tt<br />
�<br />
�� *<br />
��<br />
*<br />
�<br />
�<br />
�<br />
r N<br />
� �t *<br />
���<br />
* �<br />
*<br />
e<br />
t<br />
* � e<br />
�t<br />
0<br />
;<br />
dt<br />
dt<br />
* dt<br />
dt �<br />
Tt<br />
The value <strong>of</strong> the integral in the expression <strong>of</strong> the thermal wear depends on the parameters Δθ * and Δt * which<br />
have a symbol for a cooling process and a different one for a heating process. Thus, in the case <strong>of</strong> the heating<br />
process Δθ * is positive, and in the case <strong>of</strong> the cooling process Δθ * is negative. Consequently, the evaluation <strong>of</strong><br />
the thermal wear must be dealt with differently.<br />
dt<br />
*<br />
(25)<br />
(26)<br />
(27)<br />
(28)
6.2.1 The case <strong>of</strong> thermal heating process<br />
In the case <strong>of</strong> the thermal heating process, Δθ * being positive, the following form <strong>of</strong> expressing the heating<br />
integral Ii appears to be more convenient, employing the relation (28):<br />
�t *<br />
�e�<br />
�ln ��<br />
*<br />
�t<br />
*<br />
�<br />
�<br />
� � � *<br />
Ii<br />
� e<br />
dt<br />
0<br />
If lnΔθ * -t * is noted with x, dx=-dt * results, the expression <strong>of</strong> the integral Ii becoming:<br />
The function<br />
I<br />
51<br />
(29)<br />
ln ��<br />
*<br />
�e<br />
x<br />
i � � e dx<br />
ln ��<br />
*<br />
��t<br />
*<br />
(30)<br />
y � e<br />
is shown in the Fig. 7a the shaded area represents the value <strong>of</strong> the integral in the relation (10).<br />
�e<br />
a) b)<br />
Fig. 7. The variation <strong>of</strong> function: a) y=f(x); b) f(x).<br />
The value <strong>of</strong> the integral can be expressed as a difference between two values <strong>of</strong> the function f(x):<br />
Considering the limits <strong>of</strong> integration:<br />
x<br />
� 0 x<br />
f ( x)<br />
x<br />
* *<br />
x ln�� � �t<br />
the integral Ii can be expressed at heating as it follows:<br />
� ,<br />
� e<br />
�e<br />
x<br />
dx<br />
*<br />
0 � ln�<br />
x<br />
(31)<br />
(32)<br />
(33)
� � � � *<br />
* *<br />
ln�� � �t<br />
� ln��<br />
Ii � f<br />
f<br />
(34)<br />
The graphical representation <strong>of</strong> f(x) in relation to x is shown in Fig. 7b where the way <strong>of</strong> obtaining the integral Ii<br />
is also explained. The graphical representation requires the setting <strong>of</strong> the limits <strong>of</strong> integration x0 and xi <strong>of</strong> the<br />
heating integral Ii. The limit <strong>of</strong> integration x0 is chosen in a way that it accomplishes the condition lnΔθ *
where:<br />
Ir � g<br />
x<br />
x<br />
e �e 1�<br />
�(<br />
x)<br />
� � �<br />
x<br />
0<br />
53<br />
dx<br />
*<br />
* * * *<br />
�ln�� ��<br />
���<br />
g�ln��<br />
��<br />
��<br />
t � � �t<br />
� �t<br />
a) b)<br />
Fig. 8. The variation <strong>of</strong> the function y= e .<br />
The graphical representation <strong>of</strong> the function � (x)<br />
is shown in the Fig. 8b, illustration followed by the<br />
explanation <strong>of</strong> how the integral Ir is obtained. The random limit <strong>of</strong> integration x0, similar to the case <strong>of</strong> the<br />
heating process, depends on the sought accuracy in obtaining the value <strong>of</strong> the integral Ir. If a 1% error is<br />
accepted, it can be considered that at cooling the curve y is identical with an asymptote to which it tends<br />
(ordinate asymptote 1) when y reaches the value 1.01. The corresponding abscissa is a result <strong>of</strong> e �1,<br />
01 as<br />
being x0= - 4.6. Thus, for x
values <strong>of</strong> the constants β şi B. Fig. 9 [9] shows: curve 1 with dotted line – relation (14), corresponding to the “8<br />
degree Celsius rule”, with β=0.08664 0 C -1 ; curve 2 with dotted line - relation (14), corresponding to the “6<br />
degree rule”, with β=0.11552 0 C -1 ; curve 1 with solid line – relation (8), with B=11500 0 K; curve 2 with solid<br />
line – relation (8), with B=14573 0 K; curve 3 with solid line – relation (8), with B=17184 0 K.<br />
For all the cases the following were considered : θN=95 0 C, and TN=368 0 K, resulting ρ=1.<br />
θN and TN represent the temperature at which the degradation rate <strong>of</strong> the electroinsulant material is considered to<br />
be normal. These constants have been set starting from the hypothesis that the highest temperature admisible<br />
must allow a 25000 hour working time <strong>of</strong> the transformer, that is at a temperature <strong>of</strong> 95�C about 30 years <strong>of</strong><br />
working time. Thus, taking into consideration the lifetime laws and all the above mentioned, θN is considered to<br />
be ranging between 95 0 şi până la 98 0 C. Even 110�C is acceptable. The highest temperature admisible<br />
determines the aspect <strong>of</strong> the curves that characterise the thermal wear <strong>of</strong> the transformers [11], [13]. Regarding<br />
the transformers with oil its limit is 115�C<br />
Fig. 9. The variation curves <strong>of</strong> the thermal ageing relative factor ρ in relation to the temperature.<br />
Sometimes in cases <strong>of</strong> overvoltage conditions, this peak temperature can increase, without having negative<br />
effects on the way the transformer works though. Experiments have revealed that in cases <strong>of</strong> overvoltage the oil<br />
can reach 115�C, while the curves can reach even 200�C. This does not break the transformer if it lasts between<br />
one and four hours, but it influences its ageing process. In case <strong>of</strong> shortcircuits the temperature limit <strong>of</strong> 250�C is<br />
considered, in the hottest spot <strong>of</strong> the transformer.<br />
6.2.3 The heating process case<br />
The numerical computation <strong>of</strong> the function f(x) defined by the relation (31) allows the evaluation <strong>of</strong> the thermal<br />
ageing <strong>of</strong> the transformer in case <strong>of</strong> a heating process, the limits <strong>of</strong> integration x0 and xi being set according to<br />
the above.<br />
Thus, the limit <strong>of</strong> integration x0 is obtained from the condition:<br />
where lnΔθ*max is the peak value <strong>of</strong> Δθ* that can appear in use.<br />
X0>lnΔθ*max (42)<br />
The starting point is the hypothesis that the peak temperature <strong>of</strong> stationary regime that can appear in use is<br />
Δrlim=200 0 C. In this case, the initial temperature can be lower than that which determines a minimum thermal<br />
wear relative factor ρmin which must be taken into account. Therefore, when computing the function f(x) that<br />
minimum value <strong>of</strong> Δθ is taken into account, value which at θr=200 0 C determines a temperature <strong>of</strong> which a<br />
relative wear factor ρmin complies with. For higher values <strong>of</strong> Δθ, we will consider ρ=0 and so f(x), too. Taking all<br />
these into consideration Δθ*max will be obtained from the condition:<br />
54
� �� ���<br />
���<br />
��<br />
� N r<br />
then considering ρmin=0.1 and θr=200 0 C the following results:<br />
e<br />
55<br />
max � �<br />
min<br />
(43)<br />
Δθ*max=β(200-θN)+2.3 (44)<br />
Taking into account the relation (43) in order to obtain the highest value <strong>of</strong> Δθ*max the lowest value possible<br />
must be considered for θN and the highest for β. On the observations carried out previously we can consider the<br />
extreme values θN=95 0 C, and β=0.126 0 C -1 . We thus obtain:<br />
From the relations (41) and (44) the following results:<br />
Δθ*max=0.126*(200-95)+2.3=15.53 (45)<br />
X0=ln 15.53=2.75 (46)<br />
When x has values over 2.75, we consider f(x)=0. The lower value <strong>of</strong> the variable x that is taken into<br />
consideration is the one defined by the relation (31), namely xi= - 4.6. Fig. 10 [8] presents the variation curves<br />
for f(x), and Δθ respectively, for different values <strong>of</strong> the constant β.<br />
Fig. 10. The variation <strong>of</strong> the function f(x) and <strong>of</strong> temperature for different values <strong>of</strong> the material constant β.<br />
When using the curve f(x) the wear corresponding to the wear factors below 0.1 is neglected only in the critical<br />
case θr=θrlim. At other values <strong>of</strong> θr by using the curve f(x) the neglect <strong>of</strong> the wear appears in the case <strong>of</strong> wear<br />
factors below a critical case <strong>of</strong> ρ than 0.1. This critical case can be determined with the relation:
considering x0=2.75.<br />
56<br />
x<br />
�� ���<br />
�e<br />
0 ��<br />
��<br />
N r<br />
� lim � e<br />
(47)<br />
As established, the constant ρlim depends on the parameters β, θr, θN, but it must always be ρlim≤0,1.<br />
6.2.4 The cooling process case<br />
The numerical computation <strong>of</strong> the function φ(x) defined by the relation (39) allows the evaluation <strong>of</strong> the thermal<br />
ageing <strong>of</strong> the transformer in case <strong>of</strong> a cooling process, the limits <strong>of</strong> integration x0 and xi being set according to<br />
the above. Thus, the value <strong>of</strong> the minimum limit is x0= - 4.6. The upper limit <strong>of</strong> integration results from the<br />
condition:<br />
xS<br />
�� � �<br />
� ln �<br />
* max<br />
considering –Δθ*max as the peak value for -Δθ* that can appear in use.<br />
As shown previously, we take the hypothesis that the cooling temperature can not be higher than 140�C as<br />
starting point. Exaggeratedly considering that the cooling takes place towards 0�C, the following results –<br />
Δθ*max=140 0 C. The peak value <strong>of</strong> -Δθ* complies with the peak value <strong>of</strong> β=0.126 0 C -1 . Consequently we obtain:<br />
(48)<br />
xS=ln(0.126*140)=2.87 (49)<br />
With the limits x0 şi xs thus delimited in the Fig. 11 the variation <strong>of</strong> the function φ(x) has been featured together<br />
with that <strong>of</strong> Δθ with the help <strong>of</strong> which the evaluation <strong>of</strong> the ageing factor <strong>of</strong> the insulation <strong>of</strong> the transformer can<br />
be carried out. The function φ(x) becomes equal with zero when x=-4.6. Because when x=-4.5, φ(x)=0.001<br />
results, employing the curve in Fig. 11 [9] we will consider φ(x)=0 la x≤-4.5.<br />
Fig. 11. The variation <strong>of</strong> the function φ(x) and <strong>of</strong> size Δθ for different material constants β.
6.3. Computing examples<br />
As stated previously, the lifetime as well as the wear factor determines the state <strong>of</strong> ageing <strong>of</strong> the transformers.<br />
For example, by using the Mathcad medium, the cases <strong>of</strong> some transformers from a transformer station from<br />
Romania has been taken into consideration.<br />
1) In the case <strong>of</strong> the first transformer, to compute the wear the following initial data have been used: the initial<br />
temperature θi=78 0 C, the temperature is considered to vary exponentially with time, the stationary regime value<br />
is θr=110 0 C, the time period <strong>of</strong> the thermal process is considered to be 2.25 hours, the time constant <strong>of</strong> the<br />
thermal process is considered to be 1.5 hours. θN=95 0 C şi β=0.086643 0 C -1 are accepted, considering the “8<br />
degree Celsius rule”. The stationary regime temperature being higher than the initial temperature, and so a<br />
heating process takes place for which Δθ=110-78=32 0 C and as a consequence the f(x) curve will be used to<br />
determine the values x1 and f(x1). Therefore, on the basis <strong>of</strong> the diagram in Fig. 10 for β=0.086643 0 C -1 , the<br />
following values will be obtained: x1=1.02, f(1.02)=0.01745. Using relative values we obtain:<br />
For the limit x2 the following is obtained x2=x1-Δt * =1.02-1.5=-0.48 with which f(-0.48)=0.4376 complies.<br />
Consequently, considering the relations 28 and 33, the thermal wear will be:<br />
e<br />
u �<br />
0.<br />
086643<br />
1.<br />
5<br />
�110�95� �0. 4376 � 0.<br />
01745�<br />
�1.<br />
03<br />
As the wear u is over unity, the thermal wear for the considered time period is lower than the normal wear. From<br />
the Fig. 10, it can be established that, at the end <strong>of</strong> the time period, as x2=-0,48 complies with Δθ=7 0 C, the final<br />
temperature will be θf=110-7=103 0 C.<br />
2) In the case <strong>of</strong> the second transformer, the initial data are the following: the initial temperature θi=120 0 C, the<br />
temperature varies exponentially with the time, the stationary regime temperature is θr=85 0 C, the period <strong>of</strong> time<br />
for the thermal process is 4 hours, the time constant <strong>of</strong> the thermal process is 2 hours. θN=98 0 C şi β=0.11552 0 C -<br />
1 0<br />
are accepted, taking into consideration the six degrees rule. From the initial data, Δθ=85-120=-35 C, resulting<br />
that we are dealing with a cooling process, the function φ(x) will be employed. From the diagram φ(x), for the<br />
value β=0.11552 0 C -1 , the following results: –Δθ=35 0 * 4<br />
C, x1=1.40, φ(1,40)=18.42; in relative values: �t � � 2 .<br />
At x2=x1-Δt * =1.40-2=-0.60, in Fig. 11, we can establish φ (-0.60)=0.62. The thermal wear, computed on the<br />
basis <strong>of</strong> the relations (28) and (41), will be:<br />
0,<br />
11552<br />
e<br />
u �<br />
�85�98� 18,<br />
42 � 0,<br />
62 � 2<br />
2<br />
� � � 2,<br />
21<br />
Furthermore, with the help <strong>of</strong> the graphical representations in Fig. 11 the temperature at the end <strong>of</strong> the 4 hour<br />
period can be established. Thus, from the diagram <strong>of</strong> the function φ (x), for x2=-0.6 –Δθ=5 0 C will result and so<br />
the final temperature will be: θf=85+5=90 0 C.<br />
3) The general case in which the variation range <strong>of</strong> the constant β can be considered with the following initial<br />
data: the initial temperature θi=75 0 C, the temperature varies exponentially with time, the stationary regime<br />
temperature is θr=110 0 C and θN=95 0 C. The graphical representation <strong>of</strong> the function f(x) by reproducing the<br />
coordinates, is presented in Fig. 12.<br />
57<br />
.<br />
�t<br />
*<br />
�<br />
2,<br />
25<br />
1,<br />
5<br />
2<br />
�<br />
1,<br />
5<br />
.
Fig. 12. The variation <strong>of</strong> the function f(x).<br />
The variation <strong>of</strong> the thermal wear with the variable parameter with the help <strong>of</strong> the Mathcad program is shown in<br />
Fig. 13.<br />
Fig. 13. The variation <strong>of</strong> the thermal wear with the material constant β.<br />
Considering the same initial data we can observe the variation <strong>of</strong> the thermal wear with the temperature in Fig.<br />
14.<br />
58
Fig. 14. The variation <strong>of</strong> thermal wear with temperature.<br />
CONCLUSIONS<br />
As a result <strong>of</strong> the studies carried out, it can be stated that a number <strong>of</strong> the transformers from different transformer<br />
stations are improperly employed, that is under their real potential. An estimation <strong>of</strong> the wear <strong>of</strong> the transformers<br />
and <strong>of</strong> their ageing degree can be carried out considering the lifetime law by taking into consideration certain<br />
grounds and specific particularities:<br />
- the transformers are subject to different stresses, among which the thermal stress can be considered to be the<br />
most significant;<br />
- transformers can be considered to have a certain typical thermal behaviour;<br />
- the evaluation <strong>of</strong> the behaviour is carried out by applying the lifetime law with certain values <strong>of</strong> the constants<br />
that interfere with the law, most <strong>of</strong>ten making use <strong>of</strong> the rule <strong>of</strong> ”n” degrees. The most eloquent results have<br />
been obtained by using the “8 degree Celsius rule”;<br />
- certain load curves, <strong>of</strong> special shapes, are allowable.<br />
The thermal behaviour <strong>of</strong> transformers can be understood by means <strong>of</strong> mathematical relations, simulated through<br />
mathematical computation programme, such as the Mathcad programme. The results <strong>of</strong> the mathematical<br />
simulation can be visualised using curves and tables in which a particularization <strong>of</strong> the calculus is needed having<br />
in view: the behaviour <strong>of</strong> the transformers from a thermal point <strong>of</strong> view, the charging conditions <strong>of</strong> the<br />
transformer, the characteristics <strong>of</strong> the insulation and the evaluation method <strong>of</strong> the thermal ageing <strong>of</strong> the<br />
insulation.<br />
REFERENCES<br />
Ilie F., Bulucea C.A., Popescu M.C.,(2009), Simulations <strong>of</strong> Oil-filled Transformer Loss-<strong>of</strong>-Life Models,<br />
Proceedings <strong>of</strong> the 11 th International Conference on Mathematical Methods and Computational<br />
Techniques in Electrical Engineering (MMACTEE'09), Published by WSEAS Press, pp.195-202,<br />
Vouliagmeni Beach, Greece.<br />
Mastorakis N., Bulucea C.A., Manolea Gh., Popescu M.C., Perescu-Popescu L., (2009) Model for Predictive<br />
Control <strong>of</strong> Temperature in Oil-filled Transformers, Proceedings <strong>of</strong> the 11 th WSEAS International<br />
Conference on Automatic Control, Modelling and Simulation, pp.157-165, Istanbul, Turkey, May.<br />
Mastorakis N., Bulucea C.A., Popescu M.C., Manolea Gh., Perescu L., (2009) , Electromagnetic and Thermal<br />
Model Parameters <strong>of</strong> Oil-Filled Transformers, WSEAS Transactions on Circuits and Systems, Issue 6,<br />
Vol.8, pp.475-486, Available: http://www.worldses.org/journals/circuits/circuits-2009.htm<br />
59
Mastorakis, N.. Bulucea, C.A., Popescu M.C., (2009) Transformer Electromagnetic and Thermal Models,<br />
Proceedings <strong>of</strong> the 9 th WSEAS International Conference on Power Systems (PS`09): Advances in<br />
Power Systems, pp.108-117, Budapest, Hungary.<br />
Popescu M.C., Bulucea C.A., Perescu L., (2009) Improved Transformer Thermal Models, WSEAS Transactions<br />
on Heat and Mass Transfer, Issue 4, Vol.4, pp. 87-97, October.<br />
Available:http://www.worldses.org/journals/hmt/heat-2009.htm<br />
Popescu M.C., Manolea Gh., Bulucea C.A., Boteanu N., Perescu-Popescu L., Muntean I.O., (2009) Transformer<br />
Model Extension for Variation <strong>of</strong> Additional Losses with Frequency, Proceedings <strong>of</strong> the 11 th WSEAS<br />
International Conference on Automatic Control, Modelling and Simulation, pp.166-171, Istanbul,<br />
Turkey.<br />
Popescu M.C., Manolea Gh., Perescu L., (2009), Parameters Modelling <strong>of</strong> Transformer, WSEAS Transactions<br />
on Circuits and Systems, pp.661-675, Issue 8, Vol.8.<br />
Available:http://www.worldses.org/journals/circuits/circuits-2009.htm<br />
Popescu M.C., Mastorakis N., Bulucea C.A., Manolea Gh., Perescu L., (2009), Non-Linear Thermal Model for<br />
Transformers Study, WSEAS Transactions on Circuits and Systems, Issue 6, Vol.8, pp.487-497.<br />
Available: http://www.worldses.org/journals/circuits/circuits-2009.htm<br />
Popescu M.C., Mastorakis N., Bulucea C.A., Popescu-Perescu L., (2009) Modelling <strong>of</strong> Oil-filled Transformer,<br />
International <strong>Journal</strong> <strong>of</strong> Mathematical Models and Methods in <strong>Applied</strong> <strong>Science</strong>s, Issue 4, Vol.3, pp.346-<br />
355. Available: http://www.naun.org/journals/m3as/19-166.pdf<br />
Popescu M.C., Mastorakis N., Manolea Gh., (2009), Thermal Model Parameters Transformers, WSEAS<br />
Transactions on Power Systems, Issue 6, Vol.4, pp.199- 209,<br />
June.Available:http://www.worldses.org/journals/power/power-2009.htm<br />
Popescu M.C., Mastorakis N., Popescu-Perescu L., (2008) Electromagnetic and Thermal Model Parameters,<br />
International <strong>Journal</strong> <strong>of</strong> Energy, Issue 4, Vol.2, pp.51-65.<br />
Available: http://www.naun.org/journals/energy/19-141.pdf<br />
Popescu M.C., Mastorakis N.. Popescu-Perescu L., (2009), New Aspects Providing Transformer Models,<br />
International <strong>Journal</strong> <strong>of</strong> Systems Applications, Engineering & Development, Issue 2, Vol.3, pp.53- 63.<br />
Available: http://www.universitypress.org.uk/journals/saed/19-165.pdf<br />
Popescu M.C., Popescu C., (2009), Functional Parameters Modelling <strong>of</strong> Transformer, <strong>Journal</strong> <strong>of</strong> Mechanical<br />
Engieenering Research, pp.001-037.<br />
Available: http://www.academicjournals.org/JMER/contents/2009cont/Nov.htm.<br />
Popescu M.C., (2009), Transformer Thermal and Loss <strong>of</strong> Life Models, <strong>Journal</strong> Electrical and Electronics<br />
Engineering Research, pp.001-022.<br />
Available: http://www.academicjournals.org/JEEER/contents/2009cont/Nov.htm<br />
Popescu, M.C., Manolea, Gh., Bulucea, C.A., Perescu-Popescu, L., Drighiciu, M.A., (2009), Modelling <strong>of</strong><br />
Ambient Temperature Pr<strong>of</strong>iles in Transformer, Proceedings <strong>of</strong> the 13 th WSEAS International<br />
Conference on Circuits, (part <strong>of</strong> the 13 th WSEAS CSCC Multiconference), pp.128-137, Rodos, Greece.<br />
Stoenescu E., Popescu M.C., Bulucea C.A., Assessment <strong>of</strong> Improved Transformer Thermal Models, (2009),<br />
Proceedings <strong>of</strong> the <strong>Applied</strong> Computing Conference (ACC'09), Published by WSEAS Press, pp.189-195,<br />
Vouliagmeni Beach, Greece.<br />
60
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
A disconnect congestion detection from<br />
TCP to improve the robustness<br />
Issa Kamar and Seifeddine Kadry<br />
AUL university, Beirut, Lebanon<br />
Lebanese University - Faculty <strong>of</strong> <strong>Science</strong>, Lebanon<br />
E-mail: seifdine.kadry@aul.edu.lb, Issa.kamar@aul.edu.lb<br />
Abstract – The Transmission Control Protocol (TCP) is the most popular transport layer protocol for the internet.<br />
Congestion Control is used to increase the congestion window size if there is additional bandwidth on the network, and<br />
decrease the congestion window size when there is congestion.This paper uses a classic TCP which we called Robust<br />
TCP with an accurate algorithm <strong>of</strong> congestion detection in order to improve the performance <strong>of</strong> TCP. Our TCP Robust<br />
only reacts when it receives an ECN (Explicit Congestion Notification) mark. The evaluation result shows a good<br />
performance in the terms <strong>of</strong> drop ratio and throughput.<br />
Keywords: Congestion Control, TCP, ECN, Implicit Congestion Notification.<br />
________________________________________________________________________________________________<br />
I. INTRODUCTION<br />
TCP is a connection-oriented, end-to-end reliable protocol designed to fit into a layered hierarchy <strong>of</strong> protocols which<br />
support multi-network applications. Congestion events in communication networks cause packet losses, and it's well<br />
known that these losses occur in burst.TCP congestion control involves two tasks:<br />
1. Detect congestion<br />
2. Limit Transmission rate<br />
To achieve good performance and obtain a Robust TCP, it is necessary and important to control network congestion, by<br />
limiting the sending rate and regulating the size <strong>of</strong> congestion window (Cwnd) after the detection <strong>of</strong> congestion.TCP<br />
congestion control operates in a closed loop that infers network conditions and reacts accordingly by means <strong>of</strong> losses. A<br />
negative return is due to a loss <strong>of</strong> a segment which can be translated by decreasing the flow from the source through a<br />
reduction in the size <strong>of</strong> window control.<br />
TCP considers loss <strong>of</strong> a segment as a congestion in the network, the detection <strong>of</strong> this loss can be done in several ways:<br />
Timeout, Three Duplicate ACKs (Fast retransmit) and by receiving a partial ACK.<br />
The state is:<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
61
� If Packet Loss or congestion event =>TCP decreases Cwnd.<br />
� All is well and no congestion in the network, i.e., TCP increases Cwnd.<br />
At all cases, loss indication should be done with accuracy because it may lead to false indications like: Spurious<br />
retransmission.<br />
Spurious timeout occurs when a non lost packet is retransmitted due to a sudden RTT (Round Trip Time) increase (hand<br />
over, high delay, variability, rerouting . .) which implies to an expiration <strong>of</strong> the retransmission timer set with a previous<br />
and thus outdated RTT value.<br />
This effect is known to be the root cause <strong>of</strong> spurious retransmission.<br />
The function <strong>of</strong> the congestion control is an essential element to the stability <strong>of</strong> the internet.<br />
Indeed, TCP congestion control reduces the flow when it detects a loss in the network. Therefore, it is important to be<br />
accurate in the loss detection to improve the performance <strong>of</strong> TCP.<br />
A congestion event (or loss event) corresponds to one or several losses (or in the context <strong>of</strong> ECN: at least one<br />
acknowledgment path with an ECN-echo) occurring in one TCP window during one current RTT period, it means that a<br />
congestion event begins when the first loss occurs and finishes one RTT later.<br />
In this paper, we propose a congestion detection algorithm that is realized independently <strong>of</strong> the TCP code. To improve<br />
the TCP by reducing the Cwnd, we aim to illustrate the feasibility <strong>of</strong> the concept by demonstrating that we can both<br />
obtain similar performances and also improve the accuracy <strong>of</strong> the detection outside the TCP stack.<br />
We implement the Implicit Congestion Notification (ICN) algorithm to better understand and investigate the problem <strong>of</strong><br />
congestion events estimation.<br />
This paper is organized as follows: section 2 presents related works, section 3 shows the architecture <strong>of</strong> the congestion<br />
detection, section 4 presents the detailed discussion for the Robust TCP with ICN congestion detection algorithm, and<br />
section 5 presents an evaluation <strong>of</strong> the TCP Robust using simulations.<br />
Finally, section 6 concludes this article and presents some perspectives.<br />
II. RELATED WORKS:<br />
Over the past few years, several solutions have been proposed to improve the performance <strong>of</strong> TCP. In [5] proposed<br />
TCP-DCR modifications to TCP's congestion control mechanism to make it more robust to non-congestion events, this<br />
is implemented by using the delay "tau" based on a timer.<br />
Our mechanism is different; it relies on the accurate congestion detection algorithm (ICN) and uses the timestamp option<br />
to detect spurious timeout which can more improve the reliability <strong>of</strong> the algorithm and leads to a real Robust TCP.<br />
In Forward RTO-Recovery (F-RTO): the F-RTO algorithm <strong>of</strong> the TCP sender monitors the incoming<br />
acknowledgments to determine whether the timeout was spurious.<br />
TCP suffers from the inaccuracy <strong>of</strong> the congestion detection in the other TCP agents, for this reason we design an<br />
accurate mechanism <strong>of</strong> congestion detection (ICN) that interacts with TCP robust.<br />
Our study must prove the functionality <strong>of</strong> our TCP with ICN is better than other versions <strong>of</strong> TCP. For this point we have<br />
to show that the mechanism <strong>of</strong> congestion detection for some TCP variants (New-Reno, Sack) doesn’t detect well when<br />
there is congestion and doesn't not work well more than TCP Robust with ICN.<br />
In [5], the idea or the solution proposed for the detection <strong>of</strong> congestion is the delay <strong>of</strong> the time to infer congestion by T,<br />
and this value should be large to recover from non-congestion event, and should be small to avoid expensive RTO.<br />
Our approach is different by using a classic TCP that responds only to an accurate algorithm <strong>of</strong> congestion detection.<br />
62
III. STAND-ALONE TCP CONGESTION EVENTS ALGORITHMS<br />
In this section we present the architecture <strong>of</strong> decorrelating congestion Detection from the Transport Layer (figure 1).The<br />
main goal <strong>of</strong> this architecture is to simplify the task <strong>of</strong> kernel developers as well as improve TCP performances. This<br />
scheme opens the door to another way to react to congestion by enabling ECN emulation at end-host. In this case ICN<br />
emulates ECN marking to imply a congestion window reduction.<br />
Figure. 1. Decorrelating Congestion Detecting from the Transport Layer<br />
IV. ROBUST TCP ALGORITHM:<br />
Our proposed algorithm which we called Robust TCP is to make the congestion detection reliable and to distinguish the<br />
causes <strong>of</strong> losses in order to improve the flow control.<br />
The main idea is to determine CE (i.e. the congestion detection) which impact on the TCP flow performance by<br />
monitoring the TCP flow itself.<br />
The principle is to obtain a detection system at the edge <strong>of</strong> a network or at the sender side which analyses the TCP<br />
behavior through the observation <strong>of</strong> both data packets and acknowledgments paths.<br />
So, the scenario is to make a new version <strong>of</strong> TCP (Robust TCP) without detection <strong>of</strong> congestion. Robust TCP doesn't<br />
reacts (reducing <strong>of</strong> Cwnd) whenever it doesn't receive a notification ECN. Robust TCP must interact with ICN algorithm<br />
through ECN. Once we have congestion indication and the congestion event is validated, in this case it must notify the<br />
TCP we are exploring the functionality <strong>of</strong> Robust TCP and the ICN algorithm with the interaction between each other.<br />
Robust TCP maintains all the functions <strong>of</strong> TCP Reno (slow start, Congestion avoidance, Fast retransmit and Fast<br />
recovery) and modified by adding error control and limited transmit (like in New-Reno TCP) to avoid unnecessary<br />
timeouts.<br />
Robust TCP is a classic version <strong>of</strong> TCP but very sensitive to packet loss. It contains the major congestion control<br />
phases:<br />
1. Slow start and congestion avoidance (increase Window size).<br />
2. Fast retransmit (Detection <strong>of</strong> congestion).<br />
3. Fast recovery.<br />
1. Slow start:<br />
63
� When ACK received: cwnd++ which means for every ACK received, the sender sends two more segments.<br />
� Exponential increase in the window (Every RTT: cwnd = 2*cwnd)<br />
� Threshold (sstrhesh) controls the change to congestion avoidance.<br />
2. Congestion avoidance<br />
� When ACK received: cwnd+ = 1/cwnd.<br />
� Linear increment <strong>of</strong> cwnd (every RTT: cwnd++) slow start is exists until cwnd is smaller or equal to ssthresh.<br />
Later congestion avoidance takes over.<br />
3. Fast retransmit:<br />
TCP generates duplicate ACK when out-<strong>of</strong>-order segments are received. In this case Fast retransmit uses "duplicate<br />
ACK" to trigger retransmission packets, so the sender does not wait until timeout for retransmission, sender retransmits<br />
the missing packet after receiving 3<br />
DUPACK.<br />
4. Fast recovery:<br />
TCP retransmits the missing packet that was signaled by three duplicate ACKs and waits for an acknowledgment <strong>of</strong> the<br />
entire transmit window before returning to congestion avoidance. If there is no acknowledgment, TCP Robust<br />
experiences a timeout and enters the<br />
Slow-start state.<br />
TCP recovers much faster from fast retransmit than from timeout. When congestion window is small, the sender may not<br />
receive enough dupacks to trigger fast retransmit and has to wait for timer to expire but under<br />
Limited transmit, sender will transmit a new segment after receiving 1 or 2 DUPACKs if allowed by receivers advertised<br />
window to generate more dupacks.<br />
Robust TCP is poor in performance without detection <strong>of</strong> congestion and worse than other TCP like TCP New-Reno and<br />
Sack. It reacts only on the receiving <strong>of</strong> ECN notification.<br />
Once it doesn't receive a notification that means there is no congestion control on TCP and the window keep increasing,<br />
but in case <strong>of</strong> receiving ECN that will indicate the occurrence <strong>of</strong> congestion indication notified by ICN, than Robust TCP<br />
reacts by limiting its sending rate and takes the full meaning <strong>of</strong> its name.<br />
IV.1 ICN WITH TIMESTAMP<br />
ICN (implicit congestion notification) is an algorithm for congestion detection implemented outside the TCP stack to<br />
analyze TCP flow and to better understand the problem <strong>of</strong> congestion events and than to conclude if the congestion<br />
occurs in the network or no and it is also more accurate in congestion detection than TCP.<br />
The main goal <strong>of</strong> ICN is to determine the losses (i.e. the congestion detection) which impact on the TCP flow<br />
performance by observing the flow itself which mean by looking at the losses occurring over an RTT period given.<br />
ICN is a generic algorithm that doesn't depend on the TCP version used which implements a congestion control where a<br />
negative feedback means a loss. It is important to note that ICN doesn't manage the error control which remains under<br />
the responsibility <strong>of</strong> TCP<br />
Starting from the observation <strong>of</strong> the data segments and the acknowledgments, we identify each TCP connection with a<br />
state machine. This state machine indentifies the control congestion phase and classifies retransmission as spurious or<br />
not.TCP congestion control reacts following binary notification feedbacks allowing assessing whether the network is<br />
congested or not.<br />
ICN algorithm consists <strong>of</strong> two states:<br />
1. Normal state: which characterizes TCP connection without losses, in this state no congestion occurs and the sender<br />
receive the ACK normally.<br />
64
2. Congestion state: This state starts from the loss <strong>of</strong> the first window data segment. When a loss occurs ICN enters in<br />
this state and waits to the congestion event to be validated to notify Robust TCP about this loss. When the top <strong>of</strong> the<br />
window is acknowledged, ICN enters in the normal state.<br />
To improve the performance <strong>of</strong> the congestion detection algorithm and especially against spurious timeout we added the<br />
timestamp option, in order once the congestion happens ICN enter in this state and append a timestamp to let the sender<br />
to compute the RTT estimate based on returned timestamp in ACK.<br />
Time stamps used in this state to measure the round trip time (RTT) <strong>of</strong> a given TCP segment and including retransmitted<br />
segment, this option also can help to eliminate the retransmission ambiguity ( due to false indication) and identifies when<br />
retransmission is spurious or not.<br />
Spurious Timeout are inevitable and not rare in data networks, for this reason and once the congestion event occurs, ICN<br />
enter in the congestion event state, timestamp is added for each data segment. Timestamp can be considered as an<br />
acknowledging mechanism in the time domain.<br />
In the figure (2) shown below we will present the flowchart <strong>of</strong> TCP Robust with ICN mechanism:<br />
IV.2 Robust TCP and ICN interaction<br />
Figure 2: Robust TCP with ICN detection algorithm<br />
ICN is an accurate congestion detection algorithm where after detecting a loss event in the congestion state, the<br />
congestion event (CE) must be validated.<br />
The validation <strong>of</strong> CE should lead to a congestion indication which is the principle responsible to inform the Robust TCP<br />
about the congestion. The confirmation method due to a congestion indication is ECN (Explicit congestion notification),<br />
which is the main fag in the ACK to notify the loss to the source TCP. Once the source is signaled by ECN notification it<br />
reacts by reducing its window (Cwnd) and this time Robust TCP takes the full meaning <strong>of</strong> its name.<br />
After reducing its window, we can notice very well the decreasing <strong>of</strong> the number <strong>of</strong> dropped packets (d) in the network<br />
due to using <strong>of</strong> ICN congestion detector and our TCP becomes better in performance than others like<br />
TCP New-Reno and Sack.<br />
65
V. VALIDATIONS AND EVALUATIONS<br />
In this section we evaluate the performance <strong>of</strong> Robust TCP with ICN algorithm. The main idea is to build an algorithm <strong>of</strong><br />
congestion detection outside the TCP stack that is responsible to detect the loss and notify it to Robust TCP.<br />
The architecture <strong>of</strong> our tools is shown in the figure (3), which is mainly composed from the following components:<br />
1. Network topology.<br />
2. Traffic model.<br />
3. Performance evaluation metrics.<br />
After the simulation is done, a set <strong>of</strong> result statistics and graphs are generated.<br />
V .1 Network topology<br />
Figure 3: Architecture <strong>of</strong> our tools<br />
To study our TCP and ICN behavior we built our Network and application model shown in figure (4), in which source<br />
nodes and sink nodes connect to router 1 or router 2. The bandwidth between the two routers is much lower than the<br />
other links, which causes the link between the routers to be a bottleneck. (Traffic can be either uni-directional or<br />
bidirectional).<br />
V.2 Traffic Model<br />
Figure 4: Network topology<br />
The tool attempts to apply the typical traffic settings. In our application include the FTP traffic that uses infinite, nonstop<br />
file transmission, which begins at a random time and runs on the top <strong>of</strong> TCP. Implementation details and a<br />
comparative analysis <strong>of</strong> TCP Tahoe, Reno, New-Reno, SACK and Vegas choices <strong>of</strong> TCP variant are decided by users.<br />
V.3 Performance evaluation metrics<br />
The metrics used in our simulations are Throughput and Drop ratio. Throughput is the total elapsed flow since the<br />
beginning <strong>of</strong> simulation time. Throughput may also includes retransmitted traffic (repeated packets).Drop ratio is the<br />
total rate <strong>of</strong> packet loss during the simulation time. To obtain network statistics, we measure also the drop ratio metric<br />
that result in the failure <strong>of</strong> the receiver to decode the packet and simulation time is 100 seconds.<br />
66
Robust TCP is poor in performance as a standalone TCP but after adding the ICN it becomes much better (see figure 5)<br />
and accurate than TCP New-Reno as show in the figure (6). To evaluate our scenario, we compare TCP Robust with<br />
other TCP variants (TCP New-Reno) by using different metrics that will show us clearly the improvement <strong>of</strong> our TCP<br />
version compared to others. (Figure 6 and 7).<br />
Figure 5: Comparison between TCP Robust before and after adding ICN algorithm.<br />
The main difference between Robust and New-Reno TCP occurs in the reaction <strong>of</strong> each protocol. In the TCP New-Reno<br />
the reaction will be whenever an error or congestion occurs on the network by slowdown the transmission without being<br />
accurate if there is a congestion or not. In addition <strong>of</strong> that the main problem <strong>of</strong> New-Reno TCP that it suffers from the<br />
fact that it takes one RTT to detect each packet loss. When the ACK for the first retransmitted segment is received only<br />
then we can deduce which other segment was lost. This problem <strong>of</strong> inaccuracy in TCP New-Reno is solved by the ICN<br />
algorithm that the ICN receive the packet and check the presence <strong>of</strong> congestion by using the normal and congestion<br />
phase and by adding the timestamp option which can be make sure <strong>of</strong> the presence <strong>of</strong> congestion or no. The deduction <strong>of</strong><br />
congestion in TCP Robust is different from New-Reno, it will be deduced after signaling ECN from ICN to TCP robust,<br />
and then the TCP reacts by decreasing the transmission. This accuracy in detection <strong>of</strong> congestion can be up to 24 % as<br />
difference between the two protocols (Figure 6) before reaction <strong>of</strong> each one and starting slowdown retransmission.<br />
Due the fast reaction <strong>of</strong> TCP robust, the transmission <strong>of</strong> TCP become less than in TCP New-Reno which means that the<br />
throughput in the TCP robust must be less than in New-Reno, this is clear and deduced in the figure 7.<br />
Figure 6: Comparison between TCP Robust and TCP New-Reno<br />
67
In figure (6) represents that the drop ratio is less in Robust than in New-Reno due that TCP reacts only when receiving<br />
ECN which make its reaction faster.<br />
Figure 7: Comparison between TCP Robust and TCP New-Reno<br />
In figure (7) Robust TCP algorithm reaction is faster than the Reaction <strong>of</strong> New-Reno, thus Throughput in New-Reno is<br />
higher than when using Robust TCP. Congestion detection used by ICN algorithm is more accurate when using the<br />
timestamp option for detecting a spurious timeout which improve more the performance <strong>of</strong> TCP.<br />
The main difference between spurious timeout algorithms relies on the method how to detect spurious timeout by solving<br />
the retransmission ambiguity in many circumstances. After clarifying this ambiguity TCP can tell whether the data is there<br />
is spurious timeout has happened or not. DSACK, F-RTO and Robust TCP can see the problem <strong>of</strong> spurious timeout in<br />
different aspects.<br />
DSACK, an extension <strong>of</strong> TCP SACK, works it out in the sequence space. It requires the TCP receiver explicitly<br />
acknowledging duplicate segments with duplicate SACK options. F-RTO algorithm is used for detecting spurious<br />
retransmission timeouts with TCP. It is a TCP sender-only algorithm that does not require any TCP options to operate-<br />
RTO delays the decision <strong>of</strong> loss recovery and waits further two ACK. If the first arrived ACK forwards the sender's<br />
transmitting window, TCP concludes a spurious timeout and resume transmitting new data.<br />
Our approach is different than other TCP by using an algorithm <strong>of</strong> congestion detection outside the TCP code, where it<br />
can detect congestion and spurious timeout by using the timestamp option at the occurrence <strong>of</strong> loss or congestion event.<br />
The main advantage <strong>of</strong> ICN with timestamp algorithm is that it can work with spurious timeouts and the others loss<br />
events by detecting the congestion in the network immediately and then directly will be notified to Robust TCP in order<br />
that TCP after this action will reduce its window, which can improve very well the performance <strong>of</strong> our TCP.<br />
VI. CONCLUSION AND FUTURE WORK<br />
This paper has proposed a new algorithm, which is implemented as a stand alone component and not inside a TCP stack.<br />
This algorithm that interacts with a classic version <strong>of</strong> TCP is able to detect congestion and notify directly the loss to the<br />
Robust TCP through the congestion notification (ECN) in order to reduce its window which leads to a Robust TCP<br />
compared to other variants like New-Reno and SACK TCP. In our work we demonstrate that congestion event detection<br />
can be realized independently <strong>of</strong> the TCP code in sake <strong>of</strong> better detecting congestion occurring in the network.<br />
Following this work and the results obtained so far, we are currently planning to develop more the detection <strong>of</strong><br />
congestion by using the delay-based in the congestion detection algorithm (ICN) and the effect <strong>of</strong> fast reaction <strong>of</strong> TCP<br />
robust in the Network.<br />
68
REFERENCES<br />
A Comparative Analysis <strong>of</strong> TCP Tahoe, Reno, New- Reno, SACK and Vegas.<br />
Bhandarkar, S. and Reddy, A.L.N. (2004), Networking, May TCP-Dcr: Making TCP Robust to Non-Congestion Events.<br />
K. Ramakrishnan, S. Floyd, and D. Black, (2001), The addition to explicit congestion notification (ECN) to ip. Request<br />
for comments 3168,IETF.<br />
P. Anelli and F. Harivelo, E. lochin. On TCP congestion events detection.<br />
P.sarolahti and M. kojo. (2005), Forward rto-recovery (f-tro): An algorithm for detecting spurious retransmission<br />
timeouts with tcp and the stream control transmission protocol (sctp).rfc 4138,IETF.<br />
Reiner Ludwig and Randy H..Katz, (2000), The Eifel algorithm: making TCP robust against spurious retransmissions.<br />
SIGCOMM Comput. Common. Rev., 30(1):30-36.<br />
RFC 3649, (2003), High Speed TCP for Large Congestion Windows, S. Floyd.<br />
RFC 793, (1981), Transmission Control Protocol, September .<br />
S. Floyd, (2003), ICSI. RFC 3649 - High Speed TCP for Large Congestion Windows.<br />
69
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
ANALYSIS OF MICROWAVE SIGNAL RECEPTION USING FINITE DIFFERENCE<br />
IMPLEMENTATION. (A CASE STUDY OF AKURE – OWO DIGITAL MICROWAVE<br />
LINK IN SOUTH WESTERN NIGERIA)<br />
OTASOWIE P.O* and UBEKU E.U.<br />
Dept <strong>of</strong> Electrical /Electronic Engineering University <strong>of</strong> Benin, Benin City Nigeria.<br />
*E-mail address for correspondence : potasowie@yahoo.com<br />
______________________________________________________________________________________________<br />
Abstract: In this work, the finite difference method have been used to model microwave signal propagation. The data<br />
used for this analysis were gathered between January and December 2006 in Akure – Owo digital microwave line <strong>of</strong><br />
sight link in southwestern Nigeria.The data collected were analyzed using finite difference method and writing a<br />
program in MATLAB 7.0 s<strong>of</strong>tware program to obtain a model equation for the line <strong>of</strong> sight link. The results <strong>of</strong> the<br />
work shows that the months <strong>of</strong> August, September, July and January have the poorest signal reception while the<br />
months <strong>of</strong> February, march and April have the best signal reception in the link.The results <strong>of</strong> the predicted model<br />
were validated by measured data and the results obtained showed that the developed model can be used to accurately<br />
predict the link degradation parameters.<br />
Keywords: Microwave link, finite difference method, average signal level, signal reception.<br />
_____________________________________________________________________________________________<br />
Justification for the work<br />
INTRODUCTION<br />
Microwave signal transmission and reception in Nigeria especially for telephone services is very poor basically<br />
because <strong>of</strong> non-availability <strong>of</strong> data for planning and design <strong>of</strong> microwave links. There is a need for the build up <strong>of</strong><br />
such a database in Nigeria [1]<br />
Microwave signal propagation<br />
Microwave radio relay is a technology for transmitting digital and analog signals such as long – distance telephone<br />
calls and the relay <strong>of</strong> television programs between two locations on a line <strong>of</strong> sight radio path [ 2, 3 ]<br />
In a microwave radio relay, a line <strong>of</strong> sight link is required, therefore obstacles, the curvature <strong>of</strong> the earth, the<br />
geography <strong>of</strong> the area are important issues to consider when planning radio links.<br />
Microwave propagation hardly occur under ideal conditions, for most communication links, the analysis must be<br />
modified to account for the presence <strong>of</strong> the earth, the ionosphere and atmosphere precipitates such as fog, raindrops,<br />
snow and hail, for stations on the ground transmitting through the lower atmosphere is complicated by uncontrolled<br />
variables associated with climate weather and path terrain. Signals are said to undergo fading which refers to the fact<br />
71
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
that time – varying atmospheric processes influence the mechanisms <strong>of</strong> reflection, refraction and diffraction separately<br />
or in combination, so as to cause signal losses at a receiving antenna [3 ].<br />
Once a microwave signal is radiated by the antenna, it will propagate through space and will ultimately reach the<br />
receiving antenna. As would be expected the energy level <strong>of</strong> the signal decreases rapidly as the distance from the<br />
transmitting antenna is increased further.<br />
Mathematical Modeling<br />
The finite difference method is a full wave method <strong>of</strong> parabolic equation that directly solve a wave equation<br />
numerically subject to a number <strong>of</strong> assumptions and simplifications. The finite difference method is based on<br />
discretisation <strong>of</strong> the wave equation through the introduction <strong>of</strong> a rectangular gird and the evaluation <strong>of</strong> the various<br />
derivative terms using centered finite differences [ 4,5,6,7,8 ].<br />
The derivation <strong>of</strong> the parabolic equation normally start by reducing Maxwell’s equations to the Helmholtz equation.<br />
However in this instance if we assume the presence <strong>of</strong> an atmosphere described by a complex refractive index:<br />
n( r)<br />
� �( r)<br />
� �r<br />
( r)<br />
� j�<br />
( r)<br />
�� …………….(1.0)<br />
0<br />
which is a continuously varying function <strong>of</strong> position. Provided that � �ln n ��1,<br />
the scalar Helmholtz equation<br />
describes accurately each <strong>of</strong> the Cartesian components <strong>of</strong> the electric and magnetic fields.[,6,7]<br />
2 2 2<br />
� � � k n � � 0 ………………………(1.1)<br />
0<br />
The wave number in vacuo is now given by k 0 � 2� / �0<br />
. Considering a two dimensional propagation problem<br />
along the great circle path and making the approximation that the earth is flat over a short length for simplicity,<br />
Equation 1.1 can be expanded in Carteisian co-ordinates as:<br />
2 2<br />
� � � �<br />
� � k<br />
2 2<br />
�x<br />
�z<br />
2<br />
0<br />
2<br />
n � � 0<br />
……………….(1.2)<br />
We now introduce the assumption that an a priori preferred direction <strong>of</strong> propagation exists and identify this with the<br />
x axis. It is, therefore, reasonable that we can write the following form for the solution: [6,7]<br />
( , ) ( , ) exp( 0 ) x jk z x u z x �<br />
� � ………….(1.3)<br />
where the reduced wave amplitude u( x,<br />
z)<br />
can now be assumed to vary slowly along the x direction on the scale <strong>of</strong><br />
a free-space wavelength, � . Substituting Equation 1.3 into 1.2 and discarding the common factor exp( 0 ) x jk � after<br />
performing the differentiations yields the following equation for the reduced wave amplitude:<br />
2<br />
� u<br />
� 2 jk 2<br />
�x<br />
0<br />
2<br />
�u<br />
� u<br />
� � k 2<br />
�x<br />
�z<br />
2<br />
0<br />
( n<br />
2<br />
�1)<br />
u � 0<br />
……. (1.4)<br />
Equation 1.4 describes waves propagating both along the positive and negative x directions. By analogy with the<br />
one-dimensional wave equation<br />
2<br />
2<br />
� w 1.<br />
� w � � 1 � ��<br />
� 1 � �<br />
� � 0 �<br />
� 0<br />
2 2 2 � � ��<br />
� �w<br />
�x<br />
c �t<br />
� �x<br />
c �t<br />
��<br />
�x<br />
c �t<br />
�<br />
which has linearly independent solutions given as:<br />
w � f ( x � ct)<br />
and w � g(<br />
x � ct)<br />
……………………………. (1.5b)<br />
72<br />
0<br />
……………… (1.5a)
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
These can be identified as forward and backward traveling waves corresponding to the two<br />
differential operators in Equation 1.5a. If we factorise Equation 1.4 into forward and backward traveling wave<br />
operators; then we have<br />
…………………….(1.6)<br />
�<br />
�<br />
�<br />
�<br />
� jk<br />
� �x<br />
�<br />
� �<br />
� jk<br />
�<br />
�<br />
�x<br />
0<br />
0<br />
�<br />
�<br />
jk<br />
jk<br />
0<br />
0<br />
1�<br />
( n<br />
1�<br />
( n<br />
2<br />
2<br />
1 �<br />
�1)<br />
� 2<br />
k �z<br />
1 �<br />
�1)<br />
� 2<br />
k �z<br />
73<br />
0<br />
0<br />
2<br />
2<br />
2<br />
�<br />
�<br />
�<br />
�<br />
�<br />
�<br />
�u<br />
� 0<br />
�<br />
�<br />
If you discard the backward traveling wave for consistency with Equation 1.3, then finally, we have,<br />
�<br />
� �<br />
� jk<br />
�<br />
�<br />
�x<br />
0<br />
�<br />
jk<br />
0<br />
2<br />
2 1 �<br />
�n �1�<br />
� �u<br />
� 0<br />
1� 2 2<br />
k0<br />
�z<br />
�<br />
�<br />
�<br />
……(1.7)<br />
It is to be understood that the differential operator under the square root sign in Equation 1.7 can only be interpreted in<br />
a formal sense. Its numerical evaluation can only be achieved by replacing the square root by a power series, or<br />
rational fractions <strong>of</strong> operators.<br />
Thus, we rewrite Equation 1.4 as:<br />
�u<br />
�<br />
� jk �<br />
�x<br />
�<br />
�<br />
2<br />
2 1 � �<br />
1 � �n �1�<br />
� �u<br />
� jk �1 � 1�<br />
Q(<br />
x,<br />
z)<br />
�u ………….. (1.8)<br />
2 2<br />
k0<br />
�z<br />
�<br />
�<br />
0 1 �<br />
0<br />
The differential operator Q (x, z) must give a significantly smaller answer than the unity operator when operated on<br />
u (x,z), since by assumption, the oscillatory variation <strong>of</strong> i (x,z) is predominantly along the x direction, perpendicular to<br />
the z axis. Therefore, the z derivative on a scale <strong>of</strong> a wavelength (1/k0) is much smaller than the unity operator. For<br />
the atmosphere, we also know that n (x,z) � 1, giving: [7]<br />
Q( x,<br />
z)<br />
u(<br />
x,<br />
z)<br />
�� u(<br />
x,<br />
z)<br />
or formally ��1<br />
Q ………………………. (1.9)<br />
The simplest approximation for the square root term is given by the first two terms in its Taylor expansion, namely,<br />
1 Q( x,<br />
z)<br />
� 1�<br />
Q(<br />
x,<br />
z)<br />
/ 2<br />
� ……………….. (1.10)<br />
which finally yields the narrow-angle parabolic equation:<br />
�u<br />
�<br />
�x<br />
2 jk<br />
2 � � u<br />
�<br />
� � k 2<br />
� �z<br />
1 2<br />
0<br />
2<br />
0<br />
�<br />
�n �1�u<br />
�<br />
�<br />
�<br />
………………(1.11)<br />
Parabolic Equation – Finite difference Implementation<br />
This method is based on a more direct discretisaton <strong>of</strong> Equation 1.11, through the introduction <strong>of</strong> a rectangular grid<br />
and the evaluation <strong>of</strong> the various derivative terms using centered finite differences. The various terms appearing in<br />
Equation 1.11 are evaluated at the centre point through their finite difference discrete approximations to yield; [7,8]
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
n n<br />
u um<br />
um<br />
n<br />
x<br />
k<br />
�<br />
�1<br />
� 1<br />
( � ) �<br />
…..…………………..(1.12)<br />
� 2<br />
METHODOLOGY<br />
The line <strong>of</strong> sight microwave link used in this research work is situated between Akure located at latitude 071509.30N,<br />
longitude 0051142.60E (transmitting end) and Owo located at latitude 071220.00N longitude 0053402.00E (receiving<br />
end) over a path length <strong>of</strong> 41.42km. The Akure – Owo microwave link is owned and managed by NITEL – Nigeria<br />
Telecommunication Ltd. The microwave signal data were gathered between January and December 2006. The<br />
measurement was done with a data acquisition s<strong>of</strong>tware PROCOMM PLUS 3.0 s<strong>of</strong>tware program at the receiving<br />
end twice a week over a 24- hour period. This s<strong>of</strong>tware was installed in a computer system (laptop) type 3050 Acer<br />
Aspire. The Laptop computer system was then connected to the NITEL equipment at Owo. The PROCOMM PLUS<br />
3.0 s<strong>of</strong>tware detects and captures the received signal values in the link. The system characteristics <strong>of</strong> the Akure –<br />
Owo digital microwave link is given in Table 1.0.<br />
Table 1.0 System characteristics <strong>of</strong> the Akure – Owo digital microwave link[9]<br />
Characteristics Akure Owo<br />
Elevation (M) 348 320<br />
Latitude 071509.30N 071220.00N<br />
Longitude 0051142.60E 0053402.00E<br />
Antenna model VHP4 – VHP 4 –<br />
71W<br />
71W<br />
Antenna Height 90.00 90.00<br />
(M)<br />
Antenna Gain<br />
(dbi)<br />
Frequency (MHz) - 7500<br />
Polarization - Vertical<br />
Path length (km) - 41.42<br />
Radio Equipment model - MSM/H7 16E QPS<br />
Transmitted power (dBm) - 25.00 to 28.00<br />
Main received signal (dBm) - 45.03<br />
Received Threshold level (dBm) - 85.50<br />
36.60 36.60<br />
RESULTS AND DISCUSSION<br />
The recorded microwave signal data for the period (January to December 2006) were computed into monthly<br />
averages as shown in Table 2.0<br />
74
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 2.0 Akure – Owo Digital Microwave link, Year 2006 Average monthly data<br />
Month Received Signal Level (dBm)<br />
January - 47.0<br />
February - 36.0<br />
March - 37.0<br />
April - 36.0<br />
May - 39.0<br />
June - 39.0<br />
July - 48.0<br />
August - 50.0<br />
September - 50.0<br />
October - 46.0<br />
November - 40.0<br />
December - 47.0<br />
(i) Variation <strong>of</strong> Average Signal level with months for Year 2006<br />
The analysis <strong>of</strong> the results shows that the months <strong>of</strong> February, March and April have the best signal reception while<br />
the months <strong>of</strong> August, September and July have the poorest signal reception.<br />
(ii) Analysis <strong>of</strong> Daily signal reception using the Finite difference model<br />
The figure 1.0 shows the plot <strong>of</strong> the finite difference implementation <strong>of</strong> daily received signal level with distance.<br />
Predicted Received Signal Level for Year 2006<br />
The model equation is<br />
Y = 9x10 -32 x 8 -1.4x10 -26 x 7 + 8.8 x 10 -22<br />
- 2.9 x 10 -17 x 5 + 5.4 x 10 -13<br />
Figure 1.0: Daily microwave received signal level with distance<br />
4<br />
x – 5.5 x10 19<br />
6<br />
x<br />
3<br />
x<br />
+ 2.8 x 10 -5 x 2 – 1.0x10 -5 x + 13 ………. (1.13)<br />
If x (dBm) = Received signal level measured in equation (1.13) then Y (dBm) = predicted values.<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
For example, on Mondays 15 th February 2006, the signal transmitted was 28dbm while the signal received was -<br />
35dBm. This corresponds to the model deduced as shown in equation 1.13 that if x = 28dbm then y = -35dBm.<br />
CONCLUSION<br />
In this work microwave signal received level were measured on a monthly basis and the finite difference method was<br />
used to develop a model that can predict microwave signal received level on a daily basis.<br />
The result <strong>of</strong> the research work shows that the months <strong>of</strong> August, September, July and January have poor signal<br />
reception while the months <strong>of</strong> February, march and April have good signal reception.<br />
The model equation developed using the finite difference method is reasonably accurate.<br />
REFERENCES<br />
Akleman, F; Sevgi, L (2008) “A novel finite difference time – Domain wave propagation IEE transaction on<br />
Antennas and propagation Vol 48 No 3.<br />
Barclay, L. (2003) “Propagation <strong>of</strong> Radio waves “IEE London 2 nd Edition pp 169-177.<br />
Bogucci, J; Wielowreyska, E. (2004) “Propagation reliability <strong>of</strong> line – <strong>of</strong> – sight radio systems” 17 th International<br />
Symposium and Exhibition on Electromagnetic Compatibility Wroclaw.<br />
Isaakidis, S.A; xenos, T.D. (2004) “Progress in Electromagnetic Research” Aristotle university <strong>of</strong> Thessaloniki<br />
Greece.<br />
Landstorfer, F.M. (1999) “wave propagation models for planning <strong>of</strong> mobile communication Networks” Proceedings<br />
<strong>of</strong> the 29 th European Microwave Conference (EUMC) Vol 1<br />
Matzler, C (2004) “Parabolic Equations for wave propagation and the advanced atmospheric effects prediction<br />
systems” (AREPS) Literar seminar<br />
Nigeria Telecommunication Ltd <strong>Journal</strong> (1992) Vol 2<br />
Otasowie, P.O; Edeko, F.O. (2008) “An investigation <strong>of</strong> microwave link degradation due to Atmospheric Conditions”<br />
(A case study <strong>of</strong> Akure – Owo Digital microwave link) <strong>Journal</strong> <strong>of</strong> Advances in materials research and<br />
Systems Technologies II. Trans Tech publications Ltd Zurich Switzerland vol. 62 pp 159-165.<br />
www. Answers.com (2007) “Microwave Radio Relay 15 th February 2007.<br />
76
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Estimation <strong>of</strong> C factor for soil erosion modeling using NDVI in Buyukcekmece<br />
watershed<br />
Ahmet Karaburun<br />
Fatih University,<br />
Department <strong>of</strong> Geography,<br />
Buyukcekmece, Istanbul, 34500, Turkey<br />
E-mail address for correspondence: akaraburun@fatih.edu.tr<br />
__________________________________________________________________________________________<br />
Abstract: In order to take measures in controlling soil erosion it is required to estimate soil loss over area <strong>of</strong><br />
interest. Soil loss due to soil erosion can be estimated using predictive models such as Universal Soil Loss<br />
Equation (USLE) and Revised Universal Soil Loss Equation (RUSLE). The accuracy <strong>of</strong> these models depends on<br />
parameters that are used in equations. One <strong>of</strong> the most important parameters in equations used in both <strong>of</strong><br />
models is C factor that represents effects <strong>of</strong> vegetation and other land covers. Estimating land cover by<br />
interpretation <strong>of</strong> remote sensing imagery involves Normalized Difference Vegetation Index (NDVI), an indicator<br />
that shows vegetation cover. The aim <strong>of</strong> this study is estimate C factor values for Buyukcekmece watershed using<br />
NDVI derived from 2007 Landsat 5 TM Image. The final C factor map was generated using the regression<br />
equation in Spatial Analyst tool <strong>of</strong> ArcGIS 9.3 s<strong>of</strong>tware. It is found that north part <strong>of</strong> watershed has higher C<br />
factor values and almost 60% <strong>of</strong> watershed area has C factor classes between 0.2 and 0.4<br />
Keywords: Erosion, RUSLE, USLE, C factor, Landsat, NDVI,<br />
___________________________________________________________________________<br />
INTRODUCTION<br />
Sediment yield studies play key role for various soil and water conservation planning processes including<br />
reservoir sedimentation analysis, studies on river morphology changes and river bed siltation, and agricultural<br />
project planning. Erosion process result in soil loss from a watershed and it is difficult to estimate soil loss as it<br />
arises from a complex interaction <strong>of</strong> various hydro-geological processes (Singh et al., 2008). Estimating the soil<br />
loss risk and its spatial distribution are the one <strong>of</strong> the key factors for successful erosion assessment. Thus it can<br />
be possible to develop and implement policies to reduce the effect <strong>of</strong> soil loss under varied geographical<br />
conditions (Colombo et al., 2005). The accuracy <strong>of</strong> estimating soil risk depends on model and its factors.<br />
Researchers have developed many predictive models that estimate soil loss and identify areas where<br />
conservation measures will have the greatest impact on reducing soil loss for soil erosion assessments (Angima<br />
et al., 2003).<br />
Those models can be classified into three main categories as empirical, conceptual and physical based models<br />
(Merrit et al.,2003). USLE and its modifications are the examples <strong>of</strong> empirical models and ANSWER,<br />
CREAMS, and MODANSW are the samples <strong>of</strong> conceptual models. Examples for the first two groups comprise<br />
the empirical USLE and its modifications, and some <strong>of</strong> the more comprehensive models like ANSWERS,<br />
CREAMS, and MODANSW. ANSWERS and CREAMS are basically conceptual and eventbased. European Soil<br />
Erosion Models, EUROSEM/KINEROS, EUROSEM/MIKE SHE and SHESED-UK are the physically-based<br />
models that have been developed at catchment or small subbasin scales (Fistikoglu and Harmancioglu, 2002).<br />
Universal Soil Loss Equation (USLE) was designed to predict longtime average soil losses in run<strong>of</strong>f from<br />
specific field areas in specified cropping and management systems. The USLE (Wischmeier and Smith, 1978)<br />
estimates the average annual soil loss from:<br />
A = R.K.LS.C.P<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
where A is the estimated soil loss per year R is the run<strong>of</strong>f factor, K is the soil erodibility factor, LS is the slope<br />
length and steepness factor, C is the cover and management factor and P is the support practice factor<br />
(Wischmeier and Smith, 1978). The R factor expresses the erosivity occurring from rainfall and run<strong>of</strong>f at a<br />
particular location. An increase in the intensity and amount <strong>of</strong> rainfall results in an increase in the value <strong>of</strong> R.<br />
The K factor expresses inherent erodibility <strong>of</strong> the soil or surface material. The value <strong>of</strong> "K" is defined as a<br />
function <strong>of</strong> the particle-size distribution, organic-matter content, structure, and permeability <strong>of</strong> the soil or surface<br />
material. The LS factor expresses the effect <strong>of</strong> topography, specifically hillslope length and steepness, on soil<br />
erosion. An increase in hillslope length and steepness results in an increase in the LS factor. The C covermanagement<br />
factor is used to express the effect <strong>of</strong> plants and soil cover. Plants can reduce the run<strong>of</strong>f velocity<br />
and protect surface pores. The C-factor measures the combined effect <strong>of</strong> all interrelated cover and management<br />
variables, and it is the factor that is most readily changed by human activities. The P factor is the support<br />
practice factor. It expresses the effects <strong>of</strong> supporting conservation practices, such as contouring, buffer strips <strong>of</strong><br />
close-growing vegetation, and terracing on soil loss at a particular site. A good conservation practice will result<br />
in reduced run<strong>of</strong>f volume, velocity and less soil erosion. The USLE concept has more recently been modified<br />
and adapted by a large number <strong>of</strong> researchers by including additional data and incorporating research results.<br />
Revised Universal Soil Loss Equation (RUSLE) was developed by integrating several recent techniques and<br />
additional data that improves the accuracy <strong>of</strong> factors <strong>of</strong> USLE model (Renard and Freimund, 1994; Renard et al.<br />
1997; Yoder and Lown, 1995). Thus RUSLE was extended to include forest, rangelands and disturbed areas<br />
compared to USLE. The Revised Soil Loss Equation (RUSLE) followed the same formula as the USLE, but it<br />
has a subfactor for evaluating the cover-management factor, a new equation for slope length and steepness, and<br />
new conservation practice values. It is also applicable to non-agricultural conditions such as construction sites.<br />
The RUSLE model is widely used as a predictive model for estimating soil erosion potential and effects <strong>of</strong><br />
different management practices for over 40 years (Renard et al., 1997).<br />
One <strong>of</strong> the most important parameters in USLE and RUSLE equations is the cover management factor (C) that<br />
represents effects <strong>of</strong> vegetation and other land covers. The C factor reflects the effect <strong>of</strong> cropping and<br />
management practices on the soil erosion rate. The C factor indicates how conservation plans will affect the<br />
average annual soil loss and how that soil-loss potential will be distributed in time during construction activities,<br />
crop rotations, or other management schemes (Van der Knijff et al., 2000). Vegetation cover protects the soil by<br />
dissipating the raindrop energy before reaching the soil surface. As such, soil erosion can be effectively limited<br />
with proper management <strong>of</strong> vegetation, plant residue, and tillage (Lee, 2004). In both <strong>of</strong> USLE and RUSLE, the<br />
C factor is computed using empirical equations that contain field measurements <strong>of</strong> ground cover. (Wischmeier<br />
and Smith, 1978; Renard et al., 1997). Since the satellite image data provide up to date information on land<br />
cover, the use <strong>of</strong> satellite images in the preparation <strong>of</strong> land cover maps is widely applied in natural resource<br />
surveys (Deng et al., 2008; Serra et al.,2008; Yuan,2008).<br />
The traditional method for spatial estimation <strong>of</strong> C factor is assigning values to land cover classes using classified<br />
remotely sensed images <strong>of</strong> study areas. At the end <strong>of</strong> supervised or unsupervised classification, land cover<br />
classes are derived from image for study area and then C factors that are obtained from USLE/RUSLE guide<br />
tables or computed using field observation for each land cover classes are assigned to each pixel in land cover<br />
class (Karaburun, 2009; Efe et al., 2008; Morgan, 1995; Folly et al., 1996; Juergens and Fander, 1993). Since all<br />
pixels in a vegetation class have the same C factor value, those pixels can not represent variation <strong>of</strong> this<br />
vegetation class over the study area (Wang et al., 2002). Researchers developed many methods to estimate C<br />
factor using NDVI for soil loss assessment with USLE/RUSLE (De Jong 1994; De Jong et al., 1999; De Jong<br />
and Riezebos, 1997; Wang et al., 2002; Lin et al. 2002). These methods employ regression model to make<br />
correlation analysis between C factor values measured in field or obtained from guide tables and NDVI values<br />
derived from remotely sensed images. The unknown C factor values <strong>of</strong> land cover classes can be estimated using<br />
equation obtained from linear regression analyses. The aim <strong>of</strong> this study is to estimate C factor values <strong>of</strong> land<br />
cover classes using NDVI values by regression analysis for erosion modeling in Buyukcekmece Watershed.<br />
Study Area<br />
Buyukcekmece watershed is located in the west <strong>of</strong> Istanbul and adjacent to the Marmara Sea (Fig.1) and it<br />
contains most important water sources and a dam provides drinking water for Istanbul. The Buyukcekmece<br />
watershed is one <strong>of</strong> the largest watersheds in Istanbul having an area <strong>of</strong> about 63000 ha and located 50<br />
kilometers west <strong>of</strong> the center <strong>of</strong> Istanbul. Agriculture is one <strong>of</strong> the most dominant land use patterns in<br />
Buyukcekmece watershed, occupying about 42000 hectares <strong>of</strong> land which makes around 67 % <strong>of</strong> the total<br />
surface <strong>of</strong> watershed. Forest area <strong>of</strong> watershed is located in the west side and covers about 8000 hectares. The<br />
upper side <strong>of</strong> watershed is forest and receives annual average rainfall about 750 mm with annual average<br />
temperature 17 0 C. The climate <strong>of</strong> watershed is influenced by Mediterranean climate and Black Sea climate.<br />
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Fig.1 Study area<br />
Normalized Difference Vegetation Index (NDVI)<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
METHODOLOGY<br />
Remote sensing techniques are employed for monitoring and mapping condition <strong>of</strong> ecosystems <strong>of</strong> any part <strong>of</strong><br />
earth. Vegetation cover is the one <strong>of</strong> most important biophysical indicator to soil erosion. Vegetation cover can<br />
be estimated using vegetation indices derived from satellite images. Vegetation indices allow us to delineate the<br />
distribution <strong>of</strong> vegetation and soil based on the characteristic reflectance patterns <strong>of</strong> green vegetation. The<br />
Normalized Difference Vegetation Index (NDVI), one <strong>of</strong> the vegetation indices, measures the amount <strong>of</strong> green<br />
vegetation. The spectral reflectance difference between Near Infrared (NIR) and red is used to calculate NDVI.<br />
The formula can be expressed as (Jensen, 2000);<br />
NDVI = (NIR – red) / (NIR + red)<br />
The NDVI has been used widely in remote sensing studies since its development (Jensen, 2005). NDVI values<br />
range from -1.0 to 1.0, where higher values are for green vegetation and low values for other common surface<br />
materials. Bare soil is represented with NDVI values which are closest to 0 and water bodies are represented<br />
with negative NDVI values (Lillesand et al., 2004: Jasinski, 1990; Sader and Winne, 1992). More than 20<br />
vegetation indices have been proposed and used at present. Since NDVI provides useful information for<br />
detecting and interpreting vegetation land cover it has been widely used in remote sensing studies (Gao, 1996:<br />
Myneni and Asrar, 1994; Sesnie et al., 2008).<br />
A time-series <strong>of</strong> NDVI were derived from Landsat 5 TM images acquired on April, May, June and August 2007.<br />
An average NDVI <strong>of</strong> watershed area was calculated using those NDVI images (Fig.2).<br />
79
C Factor Estimation<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Fig.2 Average NDVI map <strong>of</strong> Buyukcekmece watershed<br />
Soil loss is very sensitive to vegetation cover with slope steepness and length factor (Renard and Ferreira 1993;<br />
Benkobi et al., 1994; Biesemans et al., 2000). Vegetation cover protects the soil by dissipating the raindrop<br />
energy before reaching soil surface. The value <strong>of</strong> C depends on vegetation type, stage <strong>of</strong> growth and cover<br />
percentage (Gitas et al., 2009). The C factor values vary between 0 and 1 based on types <strong>of</strong> land covers. Since<br />
NDVI values have correlation with C factor (De Jong, 1994; Tweddales et al., 2000; De Jong et al., 1999; De<br />
Jong and Riezebos, 1997). Many researchers used regression analysis to estimate C factor values for land cover<br />
classes in erosion assessment (Lin et al., 2002; 2006; Symeonakis and Drake, 2004; Van der Knijff et al., 2002).<br />
The goal <strong>of</strong> regression analysis is to estimate the unknown values <strong>of</strong> dependent variable based upon values <strong>of</strong> an<br />
independent variable using a mathematical model. The linear or non-linear regression equations are constructed<br />
using correlation analysis between NDVI values obtained from remotely sensed image and corresponding C<br />
factor values obtained from USLE/RUSLE guide tables or computed using field observation.<br />
Fig.3 Workflow <strong>of</strong> C factor estimating using NDVI<br />
The study assumes that there exists a linear correlation between NDVI and C factor and uses bare soil and forest<br />
NDVI values as reference values (Fig.3). Sample NDVI values were collected for bare soil and forest land cover<br />
classes from average NDVI image. Since C factor values range from 0 for well-protected soil to 1 for bare soil<br />
(Pierce et al.,1986; Vicenta et al., 2007) the C factor values for bare soil and forest land cover were set to 1 and<br />
0, respectively in the regression analysis. Fig.4 shows the graph <strong>of</strong> the regression equation. The line in Fig.4 is<br />
80
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
the regression line that describes relationship between C and NDVI values and R shows the correlation<br />
coefficient <strong>of</strong> regression analysis.<br />
The regression equation was found as;<br />
C factor = 1.02 – 1.21 * NDVI<br />
The final C factor map was generated using the regression equation in Spatial Analyst tool <strong>of</strong> ArcGIS 9.3<br />
s<strong>of</strong>tware. The graphs <strong>of</strong> regression analysis and C factor are given in Fig. 4 and Fig.5 respectively.<br />
RESULTS<br />
As can be seen from Table 1, Buyukcekmece experienced lowest mean NDVI values in August. Since watershed<br />
consists <strong>of</strong> agricultural areas the mean NDVI values <strong>of</strong> April, May and June are close to each other. Mean NVDI<br />
values <strong>of</strong> August are lowest because there is no vegetation on agricultural areas.<br />
Table 1 NDVI values <strong>of</strong> Landsat images<br />
Image Date Max NDVI Min NDVI Mean NDVI<br />
April 2007 1 -1 0,395<br />
May 2007 1 -1 0,40<br />
June 2007 1 -1 0,31<br />
August 2007 0,66 -0,43 0,09<br />
Fig.4 Linear regression <strong>of</strong> NDVI and C factor values<br />
As seen from Fig.5 the north part <strong>of</strong> watershed is represented by 0-0.1 C factor class since it is occupied by<br />
forest. Water bodies like Buyukcekmece Lake are represented by 0.9-1.0 C factor class. The agricultural areas <strong>of</strong><br />
watershed are represented by C factor classes from 0.2 to 0.4<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Fig.5 C factor map <strong>of</strong> Buyukcekmece Watershed<br />
The estimated C factor values through regression equation were divided into ten categorical classes and those<br />
classes vary between 0-0.1 and 1.0. The pixel numbers <strong>of</strong> those classes are shown in Fig.6. Since agricultural<br />
areas cover almost 60% <strong>of</strong> watershed area the C factor classes 0.2-0.3 and 0.3-0.4 contain the highest pixel<br />
number respectively. As shown in Fig.6, 0.2-0.3 class has about 28% <strong>of</strong> total pixels while 0.3-0.4 has about 15%<br />
<strong>of</strong> total pixels. The 0.9-1.0 class has the lowest pixel number.<br />
Fig.6 Pixel distribution <strong>of</strong> the C factor map based on NDVI<br />
CONCLUSION<br />
An attempt has been made to estimate C factor values <strong>of</strong> land cover classes using NDVI values for modeling soil<br />
erosion using ArcGIS 9.3 s<strong>of</strong>tware. A regression analysis was performed between NDVI and C factor using an<br />
assumption. C factor values were assigned to pixels <strong>of</strong> NDVI image through regression equation. Based on an<br />
assumption, the C factor map <strong>of</strong> Buyukcekmece watershed was produced to use in soil erosion methods such as<br />
USLE and RUSLE based on an assumption that NDVI and C factor values are correlated with each other. The<br />
results revealed that large parts <strong>of</strong> areas were assigned to C factor classes that vary between 0.2 and 0.4.<br />
It should be noted that C factor values can be precisely estimated using empirical equations that contain field<br />
measurements <strong>of</strong> land cover classes. However, this study shows that NDVI based regression method <strong>of</strong>fers an<br />
optimal method to estimate C factor values <strong>of</strong> land cover classes <strong>of</strong> large areas in a short time.<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Physiological properties studies on essential oil <strong>of</strong> Jasminum grandiflorum L. as<br />
affected by some vitamins<br />
Rawia.A.Eid, Lobna, S. Taha*, and Soad , M.M. Ibrahim<br />
Department <strong>of</strong> Ornamental Plants and Woody Trees,<br />
National Research Centre, Dokki, Cairo, Egypt<br />
*E-mail address for correspondence: lobnasalah82@yahoo.com<br />
____________________________________________________________________________________<br />
Abstract : A field experiment was conducted out during 2008 and 2009 seasons at Gezayh village, Imbaba<br />
district, Giza Governorate, Egypt. The aim <strong>of</strong> this work is to study the effect <strong>of</strong> foliar application <strong>of</strong> various<br />
concentrations (50, 100 and 150 ppm) <strong>of</strong> ascorbic acid, Thiamin and α –tocopherol separately or<br />
collectively on some flower characters (flower yield and weight <strong>of</strong> flowers), oil pattern (essential oil<br />
concrete percent, yield and some constituents <strong>of</strong> oil), physiochemical properties <strong>of</strong> oil and some chemical<br />
composition <strong>of</strong> Jasminum grandiflorum L. Promoting results were obtained with foliar application <strong>of</strong> all<br />
treatments, especially those <strong>of</strong> Ascorbic acid + Thiamin + α –tocopherol at 100 ppm <strong>of</strong> each or α –<br />
tscopherol at 150 ppm alone on flower yield, weight <strong>of</strong> flowers, oil concrete percent and oil yield as well<br />
as chemical constituents (soluble, non-soluble sugars and carbohydrates). Gas liquid chromatography <strong>of</strong><br />
the oil <strong>of</strong> control plants and those which showed increase in the oil percent revealed that the major<br />
components, i.e. Benzyl Benzoate, benzyl acetate, eugenol, trans-methyl jasmonate and cis jasmone<br />
pronouncedly increased depending on the applied vitamin (ascorbic acid, Thiamin and α –tocopherol)<br />
which also showed a stimulatory effect on physiochemical properties <strong>of</strong> oil such as refractive index,<br />
specific gravity, ester number and acid number as good conductor <strong>of</strong> oil quality.<br />
Keywords: Ascorbic acid, Thiamin , α –tocopherol, jasmin<br />
_____________________________________________________________________________________<br />
INTRODUCTION<br />
Jasmine (Jasminum grandiflorum L.) is an ornamental plant <strong>of</strong> Oleacae. It is semi-evergreen to deciduous<br />
shrub reaching a length <strong>of</strong> 8 meters, <strong>of</strong>ten with pendulous branches. The leaves are odd-pinnate wit 7 to 9<br />
leaflets and used medicinally in skin diseases, odontalgia, otalgia, wounds, etc. (Kulkarmi and Ansari,<br />
2004; Sharma et al., 2005).<br />
The flowers are white with faint, pinkish streaks, delightfully fragment, and borne in lax, terminal<br />
inflorescences. These flowers are not only essential to the perfumery industry but also have been highly<br />
appreciated by orientals since time immemorial. The pretty jasmine flower originated in the lower valleys<br />
<strong>of</strong> the Himalayas <strong>of</strong> northern India (Braja et al ., 1990). The shrub is widely cultivated in the plains and<br />
on the hills specially in Kashmir, Afghanistan, Persia, France, China, Japan and Egypt (Frank and Amelio,<br />
1999).<br />
Jasmine oil has great value for treating sever depression, respiratory tract, for muscle pain and for toning<br />
the skin. This oil is expensive. It takes approximately 800 kilos <strong>of</strong> petals or 10000 flowers, to make 1 kilo<br />
<strong>of</strong> concrete jasmine. Egypt is the main producer <strong>of</strong> jasmine oil.<br />
Plants have a small molecule antioxidants (e.g. ascorbic acid, vitamin C), glutathion and tocopherol<br />
(vitamin E) that they have signaling roles in plant development. In general, the energy metabolism<br />
pathway could be affected by one or another <strong>of</strong> these substances (Robinson, 1973; Pallanca and<br />
Smirn<strong>of</strong>f, 2000).<br />
Ascorbate is the most abundant antioxidant in plants but little was known about its biosynthesis.<br />
Smirrn<strong>of</strong>f et al., (2001) proposed a biosynthetic pathway and identified novel some enzymes. They also<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
reported that ascorbate is synthesized from L-galactose via GDP-mannose and GDP-L-galactose. El-<br />
Kobisy et a.,l (2005) stated that Ascorbic acid is synthesized in the higher plants and affects plant growth<br />
and development, it is product <strong>of</strong> D-glucose metabolism which affects some nutritional cycles activity in<br />
higher plants and play an important role in the electron transport system. Ascorbic acid (vitamin C) is<br />
known as a growth regulating factor which influences many biological processes, Price (1966). Robinson<br />
(1973) reported that Ascorbic acid acts as co-enzymatic reactions by which carbohydrates; proteins are<br />
metabolized and involved in photosynthesis and respiration processes.<br />
Ascorbic acid is an important antioxidant, which reacts not only with H2O2 but also with O2, OH and lipid<br />
hydroperoxidase (CSIR, 1992; Jacobs et al., 2000). A high level <strong>of</strong> endogenous ascorbate is essential<br />
effectively to maintain the antioxidant system that protects plants from oxidative damage (Cheruth, 2009).<br />
Tarraf et al., (1999) on lemongrass (Cympapogom citrates L.) and Farahat et al (2007) on Cupressus<br />
semperviren L. reported that foliar application <strong>of</strong> ascorbic acid caused pronounced increases in vegetative<br />
growth and chemical constituents as well as essential oil percent, oil yield per plant.<br />
Thiamin (vitamin B1) is a necessary ingredient for the biosynthesis <strong>of</strong> the coenzyme Thiamin<br />
pyrophosphate, so it plays an important role in carbohydrate metabolism. It is an essential nutrient for both<br />
plants and animals.<br />
In plants, it is synthesized in the leaves and is transported to the roots where it controls growth. Thiamin is<br />
an important c<strong>of</strong>actor for the translocation reactions <strong>of</strong> the pentose phosphate cycle, which provides<br />
pentose phosphate for nucleotide synthsis and for the reduced NADP required for various synthetic<br />
pathways (Kawasaki, 1992). Youssef and Talaat (2003) reported that pronounced increases in vegetative<br />
growth and chemical constituents <strong>of</strong> rosemary plants by foliar application <strong>of</strong> thiamine.<br />
Alpha-tocopherol (vitamin E) is low molecular weight lipophilic antioxidant which mainly protect<br />
membrane from oxidative damage (Asada, 1999). Zhang et al., (2000) reported a positive correlation<br />
between α-tocopherol and shoot or root growth in two grass species grown under drought. Tocopherols<br />
were proposed to function in relation to their antioxidant properties being prominent in protection <strong>of</strong><br />
polysaturated fatty acids from lipid peroxidation (Bosch, 1995). Recently, tocopherol had an antioxigenic<br />
property when added to green lubricating oil as rapeseed oil (Xiao et al., 2008).<br />
The aim <strong>of</strong> the present study was to reveal the best level to apply <strong>of</strong> ascorbic, thiamin and α-tocopherol<br />
which could improve the flower characters, chemical constituents and essential oil production <strong>of</strong> Jasminum<br />
grandiflorum L.<br />
Materials and methods<br />
A field experiments were conducted out at Gezayh village, Imbaba district, Giza Governorate, Egypt during<br />
two successive seasons <strong>of</strong> 2008 and 2009. The aim objective <strong>of</strong> this study was to investigate the effect <strong>of</strong><br />
foliar application <strong>of</strong> ascorbic acid, Thiamin and α –tocopherol on yield <strong>of</strong> flowers, oil pattern and chemical<br />
constituents <strong>of</strong> Jasminum grandiflorum L. cv. The investigated soil characterized by coarse sand 54%,<br />
fine sand 1%, silt 23 %, clay 22%, pH 7.5, EC 3.79 dSm -1 , and (N 35.3, P 22.6 and K 5.6 mg/100 g soil).<br />
Thirty three years old trees <strong>of</strong> jasmine were planted 2X2 m apart (1000 tree /fed). The experimental area<br />
was irrigated by flood irrigation system.<br />
Trees were sprayed twice with freshly prepared solutions <strong>of</strong> ascorbic acid, thiaminand α-tocopherol each at<br />
50, 100 and 150 ppm, and combination <strong>of</strong> the different concentrations <strong>of</strong> the three factors had been also<br />
carried out, in addition to the untreated plants (control) which were sprayed with tap water. Foliar<br />
application <strong>of</strong> ascorbic acid, thiamine and α-tocopherol carried out two times <strong>of</strong> 30 days intervals, starting<br />
at one month after March at both seasons.<br />
During the flowering period <strong>of</strong> each season, the following data were recorded: flowers yield/tree (kg) and<br />
weight <strong>of</strong> 100 flowers (g). Jasmine concrete was extracted from the flowers using a solvent extraction<br />
system <strong>of</strong> N-hexane according to Guenther (1961).<br />
Flowers are placed in vessel and covered with the solvent such as hexan, it gently heated electrically while<br />
the solvent extracts the fragments molecules <strong>of</strong> the plant. The fragment chemicals are transferred to the<br />
alcohol which is removed by low heat distillation. The essential oil was dried over anhydrous sodium<br />
sulfate and stored at 4-6 o C. The essential oil was subjected to Gc/Ms analysis and its components were<br />
identified by matching their relative retention times in conjunction <strong>of</strong> discriminating Ms ions against a<br />
computer library file <strong>of</strong> large number <strong>of</strong> data obtained under identical experimental conditions (Adams,<br />
1995). Gc/Ms Analysis was carried out on finningan Mat SSQ 7000 mass sepctometer directly coupted to<br />
a varion 3400 gas chromatography equipped with DB-5 (0.25 mm i.d. dX30m, 0.25 coating thickness,<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
fused silica capillary column using helium as the carrier gas at flow rate <strong>of</strong> 1.017 ml/min injector<br />
temperature, 220 o C transfer/line, 250 o C oven temperature programmed, 60 to 250 o C at 3 o C/min.<br />
Some jasmine oil characters i.e. refractive index at 20 o C, specific gravity at 15 o C, acid number and ester<br />
number were determined according to Guenther (1961). Also, total carbohydrates and soluble and non<br />
soluble sugars % in the flowers were estimated according to Herbert et al (1971). The recorded data<br />
(means <strong>of</strong> the two growing seasons) were statistically analyzed using the completely randomized design in<br />
factorial arrangement according to the procedure <strong>of</strong> Snedecor and Cochran (1980), where the means <strong>of</strong><br />
the studied treatments were compared using LSD test at 0.05 <strong>of</strong> probability.<br />
Flower characters<br />
RESULTS AND DISCUSSION<br />
Data presented in Table (1) reveled that all treatments <strong>of</strong> ascorbic acid, thiamine and α-tocopherol<br />
separately or collectively significantly increased flower yield/tree and weight <strong>of</strong> flowers (100 flowers (gm))<br />
<strong>of</strong> Jasminum grandiflorum L. trees compared with untreated plants. The highest increases in flower yield<br />
and fresh weight <strong>of</strong> flowers were observed in plants treated with Asc. 100 ppm + thiamin 100 ppm + αtocopherol<br />
100 ppm followed by α-tocopherol 150 ppm. The increments were 76.68 and 75.21 %, for<br />
flower yield than the corresponding values <strong>of</strong> control plants, the fresh weight <strong>of</strong> f lowers increased by 56.69<br />
and 53.42 % than the corresponding values <strong>of</strong> the control plants. Similar results were obtained by El-<br />
Quesni et al (2009) who revealed that foliar application <strong>of</strong> Ascorbic acid and α-tocopherol on Hibiscus rosa<br />
, Sineses L. plants significantly increased number <strong>of</strong> flower/plant and fresh weight <strong>of</strong> flowers gm/plant<br />
compared with untreated plants. The stimulatory effects <strong>of</strong> ascorbic acid may be attributed to its role in the<br />
regulation <strong>of</strong> cell division, differentiation and enhancement <strong>of</strong> leaf expansion (Noctor and Foyer, 1998).<br />
The effect <strong>of</strong> thiamin was showed by Kawasaki (1992) who reported that thiamin (vitamin B1) is an<br />
essential nutrient for plant growth. It is synthesized in the leaves and is translocated to the roots where it<br />
controls growth. In addition, α-tocopherol interacts with the polyunsaturated acyl groups <strong>of</strong> lipids, stabilize<br />
membranes, protect chloroplast from photooxidation and help to provide an optimal environment for<br />
photosynthetic machinery (Jaleel et a.l, 2006 and Jaleel et al., 2007).<br />
Essential oil concrete percent and oil yield<br />
Data given in Table (1) show that the foliar application <strong>of</strong> Ascorbic acid , thiamin, α-tocopherol or the<br />
combination <strong>of</strong> them significantly increased both jasmine concrete essential oil percent and oil yield as<br />
gm/tree compared to control plants. The highest increment was obtained with treatments <strong>of</strong> Ascorbic acic<br />
100 ppm + thiamin 100 ppm + α-tocopherol 100 ppm or α-tocopherol 150 ppm alone. It could be deduced<br />
from the present results that both concrete essential oil percent and oil yield (g/tree) responded to foliar<br />
application <strong>of</strong> vitamins. In support, Hasnaa et al (2009) on Pelargonium graveolens L. indicated that αtocopherol<br />
treatments at 50 and 100 mg/l significantly increased concrete essential oil percent and yield.<br />
This might be due to Alfa-tocopherol could cause a pronounced enhancement <strong>of</strong> both synthesis and<br />
accumulation <strong>of</strong> oil. Also, Gamal El-Din (2005) on sunflower plants, reported that ascorbic acid<br />
significantly increased oil percentage <strong>of</strong> seeds.<br />
Essential oil constituents<br />
Data represented in Table 2 indicates that oil <strong>of</strong> treated and control plant mainly consisted from benzyl<br />
benzaoat as major constituent (20.1-26.6 %), followed by benzyl acetate (4.8-7.7%) , benzyl alcohol (1.3-<br />
2.7%), eugenol (2.0-4.0%), trans-methyl Jasmonate (5.0-7.8%), cis jasmone (2.3-7.1%) and jasmine lactone<br />
(3.1-8.5%). On the other hand, Gas liquid chromatography showed that oil consists <strong>of</strong> other constituents<br />
such as n-acetyl and methyl anthranilate. Benzyl benzoate content was pronouncedly increased at<br />
treatment (150 ppm) <strong>of</strong> Ascorbic acid, thiamin or α-tocopherol. The highest increment was obtained with<br />
their combination treatment at concentration <strong>of</strong> 100 or 150 ppm. Similar trend was found in case <strong>of</strong> benzyl<br />
acetate, benzyl alcohol, eugenol, trans-methyl jasmonate and cis jasmone contents. However, treatment <strong>of</strong><br />
Ascorbic acid 100+ Thiamin 100 ppm + α-tocopherol 100 ppm gave the highest content <strong>of</strong> n-acetyl.<br />
Highest content <strong>of</strong> methyl anthranilate was obtained with α-tocopherol (100 ppm). These results were in<br />
agreement with those obtained by Youssef and Iman (2003) on Rosmarinus <strong>of</strong>ficinals L. who found that oil<br />
composition responded greatly to foliar spray <strong>of</strong> the vitamins nicotineamide, ascorbic and thiamin at<br />
different rates <strong>of</strong> application. Hasnaa et al., (2009) reported that Gas-liquid chromatography <strong>of</strong> the oil <strong>of</strong><br />
Pelargonium graveolens L. revealed that the major components, i.e. citronellol and linalool pronouncedly<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
increased depending on the applied stigmasterol or α-tocopherol. Therefore, one can conclude the positive<br />
response <strong>of</strong> jasmin oil constituents depended on the level <strong>of</strong> applied ascorbic acid, thiamin and αtocopherol.<br />
Essential oil physiochemical properties<br />
Results in Table 3 showed that refractive index <strong>of</strong> jasmine oil at 20 o C under treatments (ascorbic acid,<br />
thiamin, α-tocopherol and their combination) ranged from 1.41 to 1.50 in comparison with 1.3 in the<br />
control treatment. α-tocopherol (100 or 150 ppm) or Ascorbic acid + thiamin + α-tocopherol (50, 100 or<br />
150 ppm) resulted in the highest refractive index value <strong>of</strong> jasmine oil. Refractive index <strong>of</strong> oil increases<br />
with increase in the number <strong>of</strong> double bonds (iodine value). In general, the refractive indices <strong>of</strong> oils relate<br />
to the degree <strong>of</strong> unsaturation in a linear way (Rudan-Tasic & Kl<strong>of</strong>utar, 1999). Also, the specific gravity is<br />
a good indicative <strong>of</strong> purity <strong>of</strong> oil and depends on the number <strong>of</strong> double bonds. At any given temperature,<br />
specific gravity increases as the mean molecular weight decreases with increase in degree <strong>of</strong> unsaturation<br />
(higher iodine value). In our study, we can notice that specific gravity <strong>of</strong> oil under treatments ranged from<br />
0.93 to 0.99 in comparison with 0.82 in the control treatment (Table 4).<br />
Results showed that the ester no. <strong>of</strong> jasmine oil were 50.0 to 55.8 with tested treatments, compared with<br />
48.2 in the control. The acid no. <strong>of</strong> jasmine oil was 40.3 to 50.8 with various treatments, compared with<br />
45.3 in the control. The acid value is an indirect measure <strong>of</strong> free fatty acid contents present in oil. Hence it<br />
is not desirable, because they render unpleasant odor and deteriorate the quality <strong>of</strong> the product (Muhammad<br />
et al., 1999). However, the fragrance <strong>of</strong> jasmine is characterized by "jasmonoid" compounds, whose<br />
biosynthesis from unsaturated fatty acids. Under study, the results in Table 4, indicates that both Ascorbic<br />
acid and thiamin at 50, 100 and 150 ppm reduced the acid number than that <strong>of</strong> control treatment. In<br />
support, Ismail et al, 2007 indicated that refractive index <strong>of</strong> jasmine oil at 20 o C is 1.04, specific gravity <strong>of</strong><br />
oil at 15 o C is 0.4113, ester no. is 46.34 and the Acid no. <strong>of</strong> jasmine oil is 43.03 in untreated plants.<br />
Chemical constituents<br />
Data presented in Table 4 show that all treatments <strong>of</strong> Ascorbic acid, thiamin and α-tocopherol separately or<br />
collectively significantly increased soluble sugars, nonsoluble sugars and total carbohydrate %. The<br />
highest increment was observed in case <strong>of</strong> treatment Ascorbic acid + thiamin + α-tocopherol each at 100<br />
ppm followed by α-tocopherol 150 ppm. The increments were 54.6 and 52.11 % for soluble sugars, 73.29<br />
and 69.59 % for nonsoluble sugars and 48.84 and 40.78 % for total carbohydrates than the corresponding<br />
values <strong>of</strong> the control plants., these results could be explained by the findings obtained by Price (1966) who<br />
reported that ascorbic acid increased nucleic acid content, especially RNA and protein content <strong>of</strong> wheat<br />
grains. It also influenced by synthesis <strong>of</strong> enzymes, and proteins, in addition, it acts as co-enzyme in<br />
metabolic changes (Reda et al., 1977; Fadl et al, 1978 and Abdel-Halim, 1995). These results are also in<br />
agreement with those obtained by Kawasaki (1992) who reported that thiamine (vitamine B1) is a<br />
necessary ingredient for the biosynthesis <strong>of</strong> the co-enzyme thiamin pyrophosphate , in this latter form it<br />
plays an important role in carbohydrate metabolism. El-Bassiouny et al., (2005) reported that foliar spray<br />
with α-tocopherol on faba bean plant induced increments in yield components. Also , El-Quesni et al.,<br />
(2009) indicated that foliar application <strong>of</strong> Asc. acid and α-tocopherol separately to hibiscus plants<br />
significantly increased total soluble sugars through flowering stage.<br />
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Table 1: Flower characters, oil percent and oil yield (g/tree) <strong>of</strong> Jasminum grandiflorum L. plants as<br />
affected by Ascorbic acid, thiamin and α-tocopherol. (Average <strong>of</strong> the two seasons)<br />
Treatments<br />
Conc.<br />
ppm<br />
Flower yield<br />
kg/tree<br />
91<br />
Weight <strong>of</strong> 100<br />
flowers (gm)<br />
Concrete<br />
(%)<br />
Oil yield<br />
(g/tree)<br />
Control 0.87 6.8 0.13 1.13<br />
Ascorbic acid 50 1.74 8.70 0.20 3.48<br />
100 2.89 11.90 0.25 7.23<br />
150 3.15 13.40 0.29 9.14<br />
Thiamin 50 1.05 8.3 0.18 2.29<br />
100 1.85 9.0 0.23 4.26<br />
150 2.34 10.5 0.19 4.45<br />
α-tocopherol 50 2.11 10.3 0.22 4.64<br />
Ascorbic acid 50 + Thiamin 50 +<br />
α-tocopherol 50 ppm<br />
Ascorbic acid 100 + Thiamin 100 +<br />
α-tocopherol 100 ppm<br />
Ascorbic acid 150 + Thiamin 150 +<br />
α-tocopherol 150 ppm<br />
100 3.00 12.0 0.28 8.40<br />
150 3.51 14.6 0.32 11.23<br />
3.11 13.6 0.26 8.09<br />
3.73 15.7 0.34 12.68<br />
2.15 14.2 0.32 6.88<br />
LSD 5% 0.31 0.25 0.01 0.05
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 2: Major constituents <strong>of</strong> essential oil from Jasminum grandiflorum L. as affected by Ascorbic acid, thiamin and α-tocopherol.<br />
Order Retention<br />
time<br />
1 0.532<br />
(Average <strong>of</strong> the two seasons)<br />
Treatments<br />
Constituents<br />
Benzyl<br />
Benzoat&Photol<br />
Control<br />
Ascorbic acid Thiamin α-tocopherol<br />
92<br />
ppm<br />
Asorbic acid+Thiamin +<br />
α-tocopherol<br />
50 100 150 50 100 150 50 100 150 50 100 150<br />
20.1 21.2 21.5 23.0 21.5 21.5 23.0 21.5 21.8 23.4 22.5 26.5 26.6<br />
2 0.729 Benzyl Acetate 4.8 5.2 5.9 6.8 5.0 5.8 6.8 5.8 6.4 6.8 6.8 7.5 7.7<br />
3 0.838 Benzyl Alcohol 1.3 1.7 2.1 2.2 1.8 2.1 2.5 1.5 2.1 2.4 1.9 2.7 2.6<br />
4 0.919 Eugenol 2.0 2.1 2.5 2.9 2.0 3.3 2.7 2.2 2.5 3.1 2.5 3.8 4.0<br />
5 1.234<br />
Trans-methyl<br />
Jasmonates<br />
5.0 5.8 6.5 7.1 5.8 6.8 7.0 5.7 6.6 7.6 5.9 7.8 7.6<br />
6 1.641 Cis Jasmone 2.3 2.5 3.3 6.2 1.8 3.7 5.8 2.4 3.4 6.5 2.0 7.0 7.1<br />
7 1.845 Jasmine Lactone 3.1 5.5 6.2 7.4 4.3 5.7 4.5 6.5 7.4 8.5 7.0 7.9 7.5<br />
8 1.941 n-acetyl 0.81 1.0 1.5 1.8 1.1 1.3 1.6 1.4 1.8 2.2 2.2 2.5 1.9<br />
9 1.958<br />
Methyl<br />
anthranilate<br />
1.2 1.7 1.9 2.1 1.3 1.6 1.3 2.6 3.2 3.6 2.8 3.1 3.0
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 3: Physiological properties <strong>of</strong> essential oil from Jasminum grandiflorum L. as affected by Ascorbic acid, thiamin and α-tocopherol.<br />
Properties<br />
(Average <strong>of</strong> the two seasons)<br />
Treatments<br />
Control<br />
Ascorbic acid Thiamin α-tocopherol<br />
93<br />
ppm<br />
Asc.+Thiamin+<br />
α-tocopherol<br />
50 100 150 50 100 150 50 100 150 50 100 150<br />
Refractive index 20 o C 1.31 1.43 1.43 1.43 1.41 1.41 1.42 1.43 1.48 1.49 1.49 1.50 1.50 0.02<br />
Specific gravity 0.82 0.94 0.94 0.94 0.93 0.94 0.94 0.96 0.97 0.97 0.99 0.99 0.99 0.02<br />
Ester number 48.2 50.0 51.3 51.9 50.0 51.2 51.8 50.1 55.2 55.7 55.2 55.6 55.8 0.12<br />
Acid number 45.3 44.2 44.5 44.8 40.7 40.9 40.3 49.2 50.1 50.7 50.2 50.8 50.5 0.022<br />
LSD<br />
5%
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 4: Chemical constituents <strong>of</strong> Jasminum grandiflorum L.flowers (%) as affected by Ascorbic acid,<br />
thiamin and α-tocopherol. (Average <strong>of</strong> the two seasons)<br />
Treatments<br />
Conc.<br />
ppm<br />
94<br />
Soluble<br />
sugars<br />
Non-soluble<br />
sugars<br />
Total<br />
carbohydrate<br />
Control 10.2 2.11 13.2<br />
Ascorbic acid 50 15.2 2.81 19.8<br />
100 16.7 3.57 20.4<br />
150 17.9 4.11 21.5<br />
Thiamin 50 13.3 2.73 17.3<br />
100 13.2 3.84 18.4<br />
150 11.4 3.65 16.2<br />
α-tocopherol 50 17.3 3.41 20.4<br />
Ascorbic acid 50 + Thiamin 50 +<br />
α-tocopherol 50 ppm<br />
Ascorbic acid 100 + Thiamin 100 +<br />
α-tocopherol 100 ppm<br />
Ascorbic acid 150 + Thiamin 150 +<br />
α-tocopherol 150 ppm<br />
100 19.5 5.81 22.2<br />
150 21.3 6.94 22.8<br />
20.4 6.7 22.6<br />
22.5 7.9 25.8<br />
21.0 5.8 24.3<br />
LSD 5% 1.82 0.23 0.13
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
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96
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Effect <strong>of</strong> zinc and / or iron foliar application on growth and essential oil <strong>of</strong> sweet<br />
basil (Ocimum basilicum L.) under salt stress<br />
H.A.H. Said-Al Ahl* and Abeer A. Mahmoud **<br />
* Department <strong>of</strong> Cultivation and Production <strong>of</strong> Medicinal and Aromatic Plants, National Research<br />
Centre, Dokki, Giza, Egypt.<br />
** Department <strong>of</strong> Botany (Plant Physiology Section), Faculty <strong>of</strong> Agriculture, Cairo University.<br />
*Corresponding Author: saidalahl@yahoo.com<br />
___________________________________________________________________________________<br />
Abstract: The effect <strong>of</strong> salinity and Fe and/or Zn application on the vegetative growth, dry matter yield<br />
and essential oil production and its constituents were studied at the farm station <strong>of</strong> the National<br />
Research Centre, at Shalakan, Kalubia Governorate, Egypt on sweet basil (Ocimum basilicum L.)<br />
during 2006 and 2007 seasons. The highest plant height, number <strong>of</strong> branches, fresh and dry matter<br />
yield as well as essential oil yield was recorded in normal soil which decreased with the increase in the<br />
salinity. Increasing the soil salinity increased essential oil %. The addition <strong>of</strong> micronutrients had an<br />
active effect comparing with control, highest plant height and number <strong>of</strong> branches being with iron<br />
application and zinc gave the highest value <strong>of</strong> fresh weight, whereas a mixture <strong>of</strong> iron + zinc gave the<br />
highest values <strong>of</strong> dry matter and essential oil yield under normal soil condition. In contrast application<br />
a mixture <strong>of</strong> iron + zinc gave the highest essential oil % under soil salinity condition. Concerning<br />
essential oil constituents, linalool and methylchavicol were the major compounds. The concentration <strong>of</strong><br />
linalool and methylchavicol decreased with saline soil treatment. Addition <strong>of</strong> micronutrients decreased<br />
linalool in normal soil; on the contrary there was an increase in linalool content by using soil salinity<br />
treatment. Highest linalool content (52.14%) was recorded in saline soil with spraying mixture <strong>of</strong><br />
zinc+iron. Spraying plants with zinc and /or zinc+ iron increased the content <strong>of</strong> methylchavicol in<br />
normal soil, and it's content (44.01%) was the highest in normal soil with zinc spraying. All the<br />
spraying treatments except mixture <strong>of</strong> zinc+iron increased the content <strong>of</strong> methylchavicol in saline soil.<br />
The highest decrease in linalool (25.687%) and methylchavicol (20.34%) was caused with zinc+iron in<br />
normal and saline soils, respectively.<br />
Key words: sweet basil, Ocimum basilicum L., foliar application, iron, zinc, salt stress, essential oil<br />
________________________________________________________________________________<br />
INTRODUCTION<br />
The Ocimum genus, belonging to the Lamiaceae family, includes herbs and shrubs distributed in<br />
tropical and subtropical regions <strong>of</strong> Asia, Africa and the Americas. The most important species <strong>of</strong><br />
Ocimum genus is O. basilicum L.; this species, usually named common basil or sweet basil, is<br />
considered economically useful because <strong>of</strong> their basic natural characteristics as essential oil<br />
producers (Lawrence, 1993). Sweet basil is a popular culinary herb used in food and oral care<br />
products (La-Chowicz et al., 1996; Machale et al., 1997). The essential oil <strong>of</strong> the plant is also used as<br />
perfumery. Also, basil is well known as a plant <strong>of</strong> a folk medicinal used as carminative, galactogogue,<br />
stomachic and antispasmodic tonic and vermifugem, also, basil tea taken hot is good for treating<br />
nausea, flatulance and dysentery (Ozcan and Chalchat, 2002; Sajjadi, 2006). Basil is used in pharmacy for<br />
diuretic and stimulating properties, in perfumes and cosmetics for its smell; in fact, it is a part <strong>of</strong> many<br />
fragrance compositions (Bariaux et al., 1992; Khatri et al., 1995). Antiviral and antimicrobial activities<br />
<strong>of</strong> this plant have also been reported (Chiang et al., 2005). Available literature data indicates that<br />
there is a great deal <strong>of</strong> diversity in growth characteristics and the composition <strong>of</strong> essential oil <strong>of</strong> the<br />
genus Ocimum. Such observations have been attributed to the abundant cross-pollination that<br />
occurs within this genus resulting in considerable degrees <strong>of</strong> variation in the genotypes<br />
(Lawrence, 1988). The difference in the essential oil compositions in O. basilicum cultivated in<br />
different geographical localities led to the classification <strong>of</strong> basil into chemotypes on the basis <strong>of</strong> the<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
prevalent chemical components (Lawrence, 1992) or components having composition greater than<br />
20 percent (Grayer et al., 1996). There are usually considerable variations in the contents <strong>of</strong> the<br />
major components within this species. In a study <strong>of</strong> essential oils <strong>of</strong> different geographical origins,<br />
(Lawrence, 1988) found that the main constituents <strong>of</strong> the essential oil <strong>of</strong> basil are produced by two<br />
different biochemical pathways, the phenylpropanoids (methyl chavicol, eugenol, methyleugenol and<br />
methyl cinnamate) by the shikimic acid pathway, and the terpenes (linalool and geraniol) by the<br />
mevalonic acid pathway. Other latter studies on the basils from other geographical regions have<br />
added new chemotypes to that list based on the established classification scheme (Grayer,<br />
1996; Lawrence, 1992).<br />
Salinity is one <strong>of</strong> the major factors that affect plant growth; it is a serious problem in many areas <strong>of</strong><br />
world's causing considerable loss in agricultural production (Bray et al., 2000; Shao et al., 2008; Wu et<br />
al., 2007). Soil salinity resulting from natural processes or from crop irrigation with saline water,<br />
occurs in many arid and semi-arid regions <strong>of</strong> the world (Lauchli and Epstein, 1990). The deleterious<br />
effects <strong>of</strong> salinity on plant growth are associated with (1) low osmotic potential <strong>of</strong> soil solution (water<br />
stress), (2) nutritional imbalance, (3) specific ion effect (salt stress), or (4) a combination <strong>of</strong> these<br />
factors (Yildirim and Taylor, 2005). Saline soil are generally dominated by sodium ions, with the<br />
dominant anions being chloride and sulphate, they have a high sodium absorption rate with a high pH<br />
and electrical conductivities (>4 dsm -1 ) (Flowers and Flowers, 2005).<br />
In saline soils, the solubility <strong>of</strong> micronutrients is particularly low, and plants grown on such soil <strong>of</strong>ten<br />
suffer from deficiencies in these elements. Soil salinity may reduce micronutrients uptake due to<br />
stronger competition by salt cations at the root surface (Marschner and Romheld, 1994; Page et al.,<br />
1990). Soluble ferrous fe tended to become oxidized to ferric oxide which was insoluble as well as the<br />
limitation <strong>of</strong> iron uptake by root cell cytosol (Nikolic and Kastori, 2000) and inhibit iron transport to<br />
shoots and its transfer from apoplasm to cytoplasm in shoot tissues (Nikolic and Romheld, 2002). Zinc<br />
is necessary for root cell membrane integrity (Welch et al., 1982). As suggested by Parker et al. (1992),<br />
root cell membrane permeability is increased under zinc deficiency which might be related to the<br />
functions <strong>of</strong> zinc in cell membranes. From this point <strong>of</strong> view, external zinc concentrations could<br />
mitigate the adverse effect <strong>of</strong> NaCL by inhibiting Na and /or Cl uptake or translocation. Alpaslan et al.<br />
(1999) concluded that in the salt affected areas, zinc application could alleviate possible Na and Cl<br />
injury in plants. Foliar spraying under these conditions could be much more efficient than any<br />
application <strong>of</strong> nutrients to the soil (Horesh and Levy, 1981).<br />
Iron (Fe) is a c<strong>of</strong>actor for approximately 140 enzymes that catalyze unique biochemical reactions<br />
(Brittenham, 1994). Hence, iron fills many essential roles in plant growth and development, including<br />
chlorophyll synthesis, thylakoid synthesis and chloroplast development (Miller et al., 1995). Iron is<br />
required at several steps in the biosynthetic pathways. Zinc (Zn ) is an essential element for plant that<br />
act as a metal component <strong>of</strong> various enzymes or as a functional structural or regulatory c<strong>of</strong>actor and for<br />
protein synthesis, photosynthesis, the synthesis <strong>of</strong> auxin, cell division, the maintance <strong>of</strong> membrane<br />
structure and function, and sexual fertilization (Marschner, 1995).<br />
Moreover, little is known about salinity interaction with iron and zinc deprivation, the present study<br />
aimed to decrease salinity stress is a main issue in this study to ensure increasing production. Also, the<br />
present study describes the composition <strong>of</strong> the essential oils <strong>of</strong> sweet basil cultivated in Egypt.<br />
MATERIALS AND METHODS<br />
A field experiment was conducted at the farm station <strong>of</strong> the National Research Centre, at Shalakan,<br />
Kalubia Governorate, Egypt during the two successive seasons <strong>of</strong> 2006 and 2007. The physical and<br />
chemical properties <strong>of</strong> the soil sample were determined according to Jackson, 1973, Table 1.<br />
Seeds <strong>of</strong> Ocimum basilicum L. were provided by the Medicinal and Aromatic Plants Division,<br />
Horticultural Research Institute, Agricultural Research Center, Ministry <strong>of</strong> Agriculture, Egypt. The<br />
seeds <strong>of</strong> basil were sown in the nursery on 1 st March <strong>of</strong> both seasons. After 45 days from seed sowing,<br />
uniform seedlings were transplanted into plots 3x3.5m. on rows, with 60cm a part and 20 cm between<br />
the seedlings. The experimental layout was split plot design in a complete randomized block design<br />
with three replications. The main plots were devoted to the two levels <strong>of</strong> soil salinity (normal soil and<br />
saline soil), while the sub ones were assigned for three sources <strong>of</strong> second factor (Fe, Zn, and a mixture<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>of</strong> Fe + Zn). The experimental treatments consisted <strong>of</strong> 8 treatments, which represented all combinations<br />
between soil salinity conditions (normal soil, S1 = 0.73 ppm and saline soil, S2 = 4.95 ppm) and foliar<br />
application treatments (F0= control, F1= 250 ppm iron as a foliar spray <strong>of</strong> the chelated Fe-EDTA (Fe<br />
8.5%), F2= 250 ppm Zn-EDTA (Zn16%) and F3= 250 ppm mixture <strong>of</strong> zinc and iron) were sprayed at<br />
interval times <strong>of</strong> 45, 60, 120 and 150 days from transplanting.<br />
Growth characters and chemical constituent's determinations were carried out at the first and second<br />
cuts after 90 and 180 days from transplanting, respectively before flowering. The following data were<br />
recorded. Plant height (cm), number <strong>of</strong> branches / plant, fresh and dry weights <strong>of</strong> herb (g / plant or ton /<br />
feddan). The essential oil percentage was determined in the air dried herb using a modified Clevenger<br />
apparatus according to Guenther (1961). Essential oil percentage was determined and expressed as (%),<br />
while essential oil yield per plant was expressed as ml plant -1 . The essential oils <strong>of</strong> each treatment at<br />
the first and second cuts were collected and dehydrated over anhydrous sodium sulphate and kept in a<br />
refrigerator until GLC analysis. The GLC analysis <strong>of</strong> the essential oil samples was carried out in the<br />
second season using gas chromatography instrument stands at the Central Laboratory <strong>of</strong> the National<br />
Research Center with the following specifications. Instrument: Hewlett Packard 6890 series, Column:<br />
HP (Carbwax 20M) 25m length × 0.32mm I.D, Film thickness: 0.3Mm, Sample size: 1µl, oven<br />
temperature: 60-190 °C, Program: 60 °C/2min, 8 °C/min, 190 °C/25min. Injection port temperature:<br />
240 °C, Detector temperature (FID): 280 °C, Carrier gas: nitrogen, Flow rate: N2 30 ml/min; H2 30<br />
ml/min; air 300 ml/min. Main compounds <strong>of</strong> the essential oils were identified by matching their<br />
retention times with those <strong>of</strong> the authentic samples injected under the same conditions. The relative<br />
percentage <strong>of</strong> each compound was calculated from the area <strong>of</strong> the peak corresponding to each<br />
compound.<br />
Data were exposed to the proper statistical analysis <strong>of</strong> variance according to LeClerg et al. (1966) as<br />
well as Snedecor and Cochran (1990). The means represented in the study following by the same<br />
alphabetical letters were not significantly different at the probability level <strong>of</strong> 0.05, Least Significant<br />
differences (L.S.D) were used compare between means according to Waller and Duncan (1969) at<br />
probability 5%.<br />
A. Growth characters and yield<br />
Effect <strong>of</strong> soil salinity<br />
RESULTS AND DISCUSSIONS<br />
Tables (2-5) show the effect <strong>of</strong> soil salinity on plant height, number <strong>of</strong> branches, fresh and dry weights<br />
<strong>of</strong> herb (g/plant or ton/fed.) <strong>of</strong> the basil plants. These growth characters decreased significantly with<br />
soil salinity conditions in both cuts during two seasons. The inhibitory effect <strong>of</strong> salinity was also found<br />
by (Abd El-Hady, 2007; Abd El-Wahab, 2006; Baghalian et al., 2008; Belaqziz et al., 2009; Ozturk et<br />
al., 2004; Razmjoo et al., 2008; Shalan et al., 2006; Turhan and Eris, 2007). Saline conditions reduce<br />
the ability <strong>of</strong> plants to absorb water causing rapid reductions in growth rate, and induce many<br />
metabolic changes (Epstein, 1980). Also, salt stress with osmotic, nutritional and toxic effects prevents<br />
growth in many plant species (Cheeseman, 1988; Hasegawa et al., 1986). Therefore, the reduction in<br />
growth was explained by lower osmotic potential in the soil, which leads to decreased water uptake,<br />
reduced transpiration, and closure <strong>of</strong> stomata, which is associated with the reduced growth (Ben-Asher<br />
et al., 2006; Levitt, 1980). In general, the mechanisms <strong>of</strong> salinity effect on plant growth were reported<br />
by Meiri and Shalhavet (1973) who attributed the effect <strong>of</strong> salinity to the following points: (a) the<br />
distribution <strong>of</strong> salts within the plant cells may result in turgor reduction and growth retardations. Also,<br />
salinity affects root and stomatal resistance to water flow, (b) the balance between root and shoot<br />
hormones changes considerably under saline conditions, (c) salinity changes the structure <strong>of</strong> the<br />
chloroplasts and mitochondria and such changes may interfere with normal metabolism and growth, (d)<br />
salinity increases respiration and reduces photosynthesis products available for growth.<br />
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Effect <strong>of</strong> micronutrients<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Basil plants sprayed with zinc and/or iron under normal and saline soils conditions were superior if<br />
compared without sprayed plants (tables, 2-5). Results also indicated that treated plants with iron were<br />
much superior in plant height and number <strong>of</strong> branches compared with other treatments. However,<br />
plants treated by zinc were produced fresh and dry weights <strong>of</strong> herb (g/plant or ton/fed.) greater than<br />
those other treatments. While, plants treated with mixture <strong>of</strong> zinc and iron gave the heaviest dry weight<br />
in the first cut, but treated plants with zinc or iron were produced dry weights <strong>of</strong> herb greater than those<br />
<strong>of</strong> other treatments in the second cut during first and second seasons, respectively. The stimulatory<br />
effect <strong>of</strong> zinc and/or iron were recorded by (Aziz and El- Sherbeny, 2004; Pande et al., 2007; Said-Al<br />
Ahl, 2005; Said-Al Ahl and Omer, 2009).<br />
The stimulation effects <strong>of</strong> applying zinc and iron on vegetative growth may be attributed to the well<br />
known functions <strong>of</strong> zinc and iron in plant life, as described in the Introduction. Moreover, zinc is a<br />
component <strong>of</strong> carbonic anhydrase, as well as several dehydrogenases and auxin production which in<br />
turn enhanced the elongation processes, besides the function <strong>of</strong> zinc in CO2 assimilation. Consequently,<br />
the fresh and dry weights <strong>of</strong> herb could be increased (Marschner, 1995). However, iron deficiency<br />
inhibited leaf growth, cell number, size and cell division, as well as chlorophyll, protein, starch and<br />
sugar content. Thus, the fresh and dry weights <strong>of</strong> herb could be decreased. Iron is necessary for the<br />
biosynthesis <strong>of</strong> chlorophyll and cytochrome, besides the function <strong>of</strong> iron in the metabolism <strong>of</strong><br />
chloroplast RNA, leading to increase in the biosyntheses materials (produced and accumulated),<br />
consequently, the growth was enhanced (Marschner, 1995).<br />
Effect <strong>of</strong> interaction<br />
The interaction between normal soil and saline soil conditions with zinc and/or iron application<br />
resulted in a significant increment <strong>of</strong> plant height and number <strong>of</strong> branches in the two cuts for both<br />
seasons (Tables, 2-5). Fresh weight <strong>of</strong> herb (g/plant or ton/fed.) was significantly increased in the<br />
second cut and non significant in the first cut in both seasons, but dry weight <strong>of</strong> herb (g/plant or<br />
ton/fed.) increased significantly in both cuts, except, this increment was insignificant in the second cut<br />
at first season. The maximum plant height and number <strong>of</strong> branches mean values were recorded from<br />
the combination <strong>of</strong> iron spraying and non soil salinity in all cuttings <strong>of</strong> both seasons. The highest fresh<br />
and dry weights <strong>of</strong> herb (g/plant or ton/fed.) resulted from zinc spraying and non soil salinity, or<br />
mixture (zinc and iron) spraying and non soil salinity, respectively in all cuttings <strong>of</strong> both seasons.<br />
While, the minimum growth characters values were resulted from the soil salinity condition without<br />
any treatment.<br />
B. Essential oil production<br />
Effect <strong>of</strong> soil salinity<br />
Tables (4, 5) explain that soil salinity conditions significant increased essential oil %. The increase in<br />
essential oil % due to salinity conditions was found by (Al-Amier and Craker, 2007; Baghalian et al.,<br />
2008; Baher et al., 2002; Hendawy and Khalid, 2005; Prasad et al., 2006; Tabatabale and Zari, 2007).<br />
In contrast, essential oil yield was significant decreased at the first and second cuts <strong>of</strong> both seasons.<br />
The results were similar in both the two seasons. Similar results were found by (Abd El-Wahab, 2006;<br />
Baghalian et al., 2008; Ozturk et al., 2004; Razmjoo et al., 2008). The reduction <strong>of</strong> essential oil yield<br />
by salinity due to a decrease in growth characters.<br />
The stimulation <strong>of</strong> essential oil production under salinity could be due to a higher oil gland density and<br />
an increase in the absolute number <strong>of</strong> glands produced prior to leaf emergence (Charles et al., 1990).<br />
Salt stress may also affect the essential oil accumulation indirectly through its effects on either net<br />
assimilation or the partitioning <strong>of</strong> assimilate among growth and differentiation processes (Charles et<br />
al., 1990).<br />
Penka (1978) showed that the formation and accumulation <strong>of</strong> essential oil in plants was explained as<br />
due to the action <strong>of</strong> environmental factors. It might be claimed that the formation and accumulation <strong>of</strong><br />
essential oil was directly dependent on perfect growth and development <strong>of</strong> the plants producing oils.<br />
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The decrease in oil production might be due to the decrease in plant anabolism. Morales et al. (1993)<br />
suggested that, an increase in oil content in some <strong>of</strong> the salt stressed plants might be attributed to<br />
decline the primary metabolites due to the effects <strong>of</strong> salinity, causing intermediary products to become<br />
available for secondary metabolites synthesis.<br />
Effect <strong>of</strong> micronutrients<br />
Data in Tables (4, 5) indicate that the essential oil (% or yield) <strong>of</strong> basil sprayed with zinc + iron was<br />
higher than the other treatments, followed by plants treated with zinc, and then plants treated with iron,<br />
whereas plants untreated (control) was lower in this respect in the two cuts during the two seasons. The<br />
increase in essential oil due to zinc and /or iron was also found by (El-Sawi and Mohamed, 2002;<br />
Maurya, 1990; Pande et al., 2007; Said-Al Ahl, 2005; Said-Al Ahl and Omer 2009; Subrahmanyam et<br />
al., 1992). From previous studies, biosynthesis <strong>of</strong> secondary metabolites is not only controlled<br />
genetically but it also is affected strongly by environmental influences (Naghdi Badi et al., 2004). In<br />
line with the foregoing, environmental variables affect essential oil, Marschner (1995) found that iron<br />
has important functions in plant metabolism, such as activating catalase enzymes associated with<br />
superoxide dismutase, as well as in photorespiration and the glycolate pathway. Also, in iron-deficient<br />
plants, the activities <strong>of</strong> some enzymes are impaired and may <strong>of</strong>ten be responsible for gross changes in<br />
metabolic processes. Moreover, zinc is an essential micronutrient that acts either as a metal component<br />
<strong>of</strong> various enzymes or as a functional, structural, or regulatory c<strong>of</strong>actor associated with saccharide<br />
metabolism, photosynthesis, and protein synthesis (Marschner, 1995). Carbon dioxide and glucose are<br />
precursors <strong>of</strong> monoterpene biosynthesis. Saccarides are also a source <strong>of</strong> energy and reducing power for<br />
terpenoid synthesis. As zinc is involved in photosynthesis and saccaride metabolism, and as CO2 and<br />
glucose is the most likely sources <strong>of</strong> carbon utilized in terpene biosynthesis, the role <strong>of</strong> zinc in<br />
influencing essential oil accumulation seems particularly important (Srivastava et al., 1997).<br />
Effect <strong>of</strong> interaction<br />
From data in Tables (4, 5), it can be concluded that the interaction treatments between foliar spray with<br />
micronutrients (Zn, Fe and mixture <strong>of</strong> Zn + Fe) and soil salinity significantly increased essential oil %<br />
and essential oil yield in both cuts during two seasons, except essential oil % at first cut was increased<br />
insignificantly <strong>of</strong> both seasons if comparing with none and soil salinity conditions. The highest value <strong>of</strong><br />
essential oil % was obtained by spraying with zinc + iron under soil salinity conditions. Whereas,<br />
plants sprayed with zinc + iron under none soil salinity gave the highest value <strong>of</strong> essential oil yield in<br />
both cuts during two seasons.<br />
C. Chemical composition <strong>of</strong> essential oils<br />
Table (6) show the data belonging to qualitative and quantitative constituents <strong>of</strong> essential oils distilled<br />
from the basil herb before flowering stage collected from the first and second cuts during the season <strong>of</strong><br />
2007. The essential oil composition <strong>of</strong> 8 treatments, along with the quantitative data is listed in Table 6.<br />
Twenty-four compounds were identified. Comparison <strong>of</strong> the analytical data <strong>of</strong> the oils revealed marked<br />
differences in qualitative and quantitative composition. Considering the main components, <strong>of</strong> the all<br />
treatments were characterized by high contents <strong>of</strong> linalool (38.28-52.14%) and methylchavicol (20.34-<br />
27.67%), and moderate amounts <strong>of</strong> 1,8-cineol (6.04-9.22%), germacrene D (2.32-4.38%), and very<br />
variable amounts <strong>of</strong> cis-bisabolene (0.00-2.53%), geraniol (0.59-2.02%), nerol (0.89-1.78%), cadinol<br />
(0.00-1.75%) and 1,4 terpineol (0.66-1.70%), and a lower amounts <strong>of</strong> α-thujene, β-pinene, α-pinene,<br />
camphene, sabinene, myrcene, ocimene, limonene, selinene, nerolidole, cadinene, caryophyllene,<br />
eugenol, camphor and α-terpinene considered as traces.<br />
The results in table (6) show that iron treatment gave the highest content <strong>of</strong> (methylchavicol,<br />
germacrene D, α-pinene and α-thujene); zinc treatment gave the highest content <strong>of</strong> (1, 8-cineol, βpinene,<br />
camphor, nerolidole and camphene) as well as iron + zinc treatment gave the highest content <strong>of</strong><br />
(linalool, sabinene, nerol, eugenol, selinene and cadinole). However, control treatment gave the same<br />
result <strong>of</strong> (limonene, α-terpinene, 1,4 terpineol, caryophyllene, cis-bisabolene, cadinene and ocimene)<br />
under the soil salinity conditions.<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
According to major compounds it was obviously cleared that soil salinity treatment decreased both <strong>of</strong><br />
linalool and methylchavicol compared to that <strong>of</strong> control Also, linalool was decreased with spraying<br />
treatments comparing to that <strong>of</strong> control, while there was an increase in methylchavicol by using zinc<br />
and mixture <strong>of</strong> zinc + iron whereas iron treatment had the lowest in this regard comparing to that <strong>of</strong><br />
control in normal soil. However, under saline soil condition, the results indicate that linalool was<br />
increased with spraying treatments comparing to that <strong>of</strong> control and mixture <strong>of</strong> iron + zinc followed by<br />
zinc and then iron gave the highest content <strong>of</strong> linalool. Whereas, methyl chavicol was increased with<br />
spraying <strong>of</strong> iron and zinc, but decreased by iron + zinc comparing to that <strong>of</strong> control and iron followed<br />
by zinc and then control treatment gave the highest content <strong>of</strong> methylchavicol. The highest content <strong>of</strong><br />
linalool was obtained by using zinc + iron under saline soil compared to the other interaction ones and<br />
the lowest value in this respect obtained in normal soil from the same treatment. However, zinc<br />
treatment gave the highest content <strong>of</strong> methylchavicol in normal soil but, under soil salinity, zinc+iron<br />
treatment gave the lowest value in this respect in all cases.<br />
The present study was in accordance by EL-Keltawi and Croteau (1987) on spearmint and marjoram<br />
who indicated that irrigation <strong>of</strong> both plants with saline solution consisting <strong>of</strong> calcium chloride and<br />
sodium chloride reduced essential oil. They added that under salinity in spearmint the content <strong>of</strong><br />
limonene was increased and carvone was concomitantly decreased relative to controls irrigated with<br />
water only. In case <strong>of</strong> marjoram, salt stress led to increase the content <strong>of</strong> sabinene which was<br />
accompanied by a decrease in the content <strong>of</strong> sabinene hydrate. Hendawy and Khalid (2005) on salvia<br />
<strong>of</strong>ficinalis reprted that treatment <strong>of</strong> 2500 ppm soil salinity increased α–thujone, camphor and 1,8-<br />
cineol but it decreased the component <strong>of</strong> β–thujone compared with the control treatment.<br />
Said-Al Ahl and Omer (2009) indicated that linalool was increased in the herb and seeds <strong>of</strong> coriander,<br />
but dodecenal <strong>of</strong> herb was decreased with treatment <strong>of</strong> zinc and mixture <strong>of</strong> zinc + iron compared to<br />
control. Also, Said-Al Ahl et al. (2010) indicated that soil salinity treatments at 1500 and 4500 ppm<br />
levels increased the content <strong>of</strong> linalool and on the contrary there was decreased in eugenol content by<br />
using 1500 and 4500 ppm <strong>of</strong> soil salinity in the Ocimum basilicum var. purpurascens.<br />
The essential oil <strong>of</strong> basil in this study belonging to linalool and methylchavicol chemotype,<br />
characterized by the simultaneous presence <strong>of</strong> linalool and methylchavicol, can be ascribed to those<br />
plants in which essential oil constituents are produced by two different biosynthetic pathways. In fact,<br />
methylchavicol has a common biosynthesis originating from the precursor (L-phenylalanine and<br />
cinnamic acid), whereas linalool follows another biogenetic pathway from mevalonic acid via geranyl<br />
pyrophosphate (Nikanen, 1989). It is known that climatic conditions and water available in the soil can<br />
change the vegetal secondary metabolism and, consequently ,alter the composition <strong>of</strong> essential oils,<br />
throughout the seasons <strong>of</strong> the year. Chemical variations in essential oils were associated with seasons<br />
for Ocimum selloi (Moraes et al., 2002) and with time <strong>of</strong> day for Ocimum gratissimum (Vasconcelos<br />
Silva et al., 1999(.<br />
.<br />
Table 1. The physical and chemical properties <strong>of</strong> the experimental soil.<br />
Physical and chemical properties Normal soil Saline soil<br />
Sand (%) 46.8 49.6<br />
Silt (%) 28.2 26<br />
Clay (%) 25.0 24.4<br />
Soil texture Sandy loam Sandy loam<br />
pH 8.12 8.45<br />
E.C (m. mohs/cm) 0.73 4.95<br />
Organic matter (%) 0.95 0.40<br />
N (mg kg -1 ) 0.09 0.05<br />
P (mg kg -1 ) 20.0 0.45<br />
K (mg kg -1 ) 208.0 2.04<br />
Zn (ppm) 1.2 0.65<br />
Iron (ppm) 20.0 1.32<br />
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Table 2. Effect <strong>of</strong> soil salinity, foliar spray with micronutruients and their interactions on plant height, branches number and herb fresh weight <strong>of</strong> Ocimum<br />
basilicumL. plants at first cut in 2006 and 2007 seasons.<br />
Treatments<br />
Plant height (cm) Branches number plant -1 Fresh weight g plant -1<br />
Season 1 Season 2 Season 1 Season 2 Season 1 Season 2<br />
S1 55.43 a ± 7.831 55.61 a ± 7.972 11.91 a ± 2.188 11.24 a ± 1.898 110.44 a ± 9.481 110.24 a ± 10.077<br />
S2 36.27 b ± 3.939 37.11 b ± 5.451 7.18 b ± 1.395 7.68 b ± 1.589 54.43 b ± 6.849 53.25 b ± 5.940<br />
LSD at � 0.05 5.1220 0.6758 2.2470 1.0230 6.0970 7.8010<br />
F0 38.24 d ± 6.538 37.45 d ± 7.113 7.68 c ± 2.891 7.23 c ± 2.285 71.25 b ± 28.708 69.83 b ± 28.388<br />
F1 52.69 a ± 12.539 53.69 a ± 10.499 11.10 a ± 3.705 11.17 a ± 2.792 85.27 a ± 29.959 84.00 a ± 30.361<br />
F2 44.15 c ± 11.738 44.04 c ± 11.247 9.29 b ± 1.385 9.46 b ± 0.499 88.43 a ± 33.338 87.52 a ± 33.179<br />
F3 48.32 b ± 11.649 50.25 b ± 12.007 10.10 ab ± 3.188 9.99 b ± 2.357 84.80 a ± 31.976 85.63 a ± 33.696<br />
LSD at � 0.05 1.8820 2.0190 1.0550 0.5440 6.9310 4.5900<br />
S1xF0 44.07 d ± 2.001 43.87 c ± 0.998 10.15 c ± 1.550 9.29 cd ± 0.543 97.17 ± 4.908 95.50 ± 5.500<br />
S1xF1 64.09 a ± 0.460 63.17 a ± 1.607 14.40 a ± 1.058 13.70 a ± 0.265 112.33 ± 4.646 111.50 ± 5.074<br />
S1xP2 54.73 c ± 2.194 54.22 b ± 1.338 10.18 c ± 1.154 9.89 c ± 0.271 118.60 ± 5.769 117.63 ± 5.119<br />
S1xF3 58.83 b ± 2.021 61.17 a ± 1.607 12.90 b ± 1.258 12.07 b ± 0.902 113.67 ± 5.508 116.33 ± 3.215<br />
S2x F0 32.42 g ± 1.040 31.03 e ± 1.380 5.20 e ± 0.346 5.17 f ± 0.153 45.33 ± 4.619 44.17 ± 2.843<br />
S2xF1 41.29 e ± 1.728 44.20 c ± 1.814 7.80 d ± 0.721 8.63 de ± 0.404 58.20 ± 4.952 56.50 ± 3.148<br />
S2xF2 33.56 g ± 1.822 33.87 e ± 1.963 8.40 d ± 1.039 9.04 d ± 0.063 58.27 ± 3.900 57.41 ± 2.342<br />
S2 xF3 37.80 f ± 1.836 39.33 d ± 0.577 7.30 d ± 0.520 7.90 e ± 0.173 55.93 ± 5.100 54.93 ± 0.902<br />
LSD at � 0.05 2.6620 2.8550 1.4920 0.7693 N.S N.S<br />
Means with different letters within each column are significant at 0.05 level and means in the same column with the same letters are not significant. Mean<br />
±Sd (standard deviation)<br />
Since: S = Soil salinity, i. e. S1 = 0.73 dsm -1 , S2 =4.95 dsm -1 ; F = Foliar spray with micronutrients, i. e. F0 = control, F1 = iron 250ppm, F2 = zinc 250ppm,<br />
F3= mixture <strong>of</strong> iron + zinc<br />
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Table 3. Effect <strong>of</strong> soil salinity, foliar spray with micronutruients and their interactions on plant height, branches number and herb fresh weight <strong>of</strong> Ocimum<br />
basilicum L. plants in at second cut in 2006 2007 seasons.<br />
Treatments<br />
Plant height (cm) Branches number plant -1 Fresh weight g plant -1<br />
Season 1 Season 2 Season 1 Season 2 Season 1 Season 2<br />
S1 70.53 a ± 7.733 69.46 a ± 7.137 15.41 a ± 1.874 14.79 a ± 2.192 138.78 a ± 15.292 133.63 a ± 12.583<br />
S2 51.08 b ± 5.595 51.75 b ± 5.683 11.03 b ± 2.116 11.17 b ± 2.248 67.75 b ± 9.697 71.65 b ± 11.697<br />
LSD at � 0.05 3.3340 1.9350 1.3940 2.2600 5.3080 2.7990<br />
F0 53.17 c ± 7.047 51.70 d ± 7.200 10.63 c ± 2.815 10.38 b ± 2.681 84.81 c ± 35.643 84.58 d ± 32.444<br />
F1 69.32 a ± 10.901 68.02 a ± 8.634 14.44 a ± 3.247 14.18 a ± 2.717 106.50 b ± 35.681 107.30 b ± 30.040<br />
F2 59.01 b ± 12.088 60.36 c ± 10.843 13.95 ab ± 0.580 13.48 a ± 0.949 116.50 a ± 45.873 114.67 a ± 34.373<br />
F3 61.70 b ± 13.336 62.35 b ± 12.282 13.84 b ± 3.299 13.88 a ± 3.279 105.25 b ± 38.621 104.00 c ± 39.100<br />
LSD at � 0.05 2.9820 1.2510 0.5352 0.9621 1.9870 2.6340<br />
S1xF0 59.47 c ± 1.295 58.23 e ± 0.979 13.20 c ± 0.200 12.70 bc ± 1.082 117.29 c ± 2.350 114.17 d ± 1.443<br />
S1xF1 79.01 a ± 2.968 75.87 a ± 0.594 17.39 a ± 0.344 16.50 a ± 1.323 139.00 b ± 1.000 134.67 c ± 2.517<br />
S1xP2 69.89 b ± 1.723 70.22 c ± 1.235 14.23 b ± 0.521 13.09 bc ± 1.299 158.33 a ± 2.887 146.00 a ± 2.000<br />
S1xF3 73.73 b ± 2.802 73.53 b ± 0.924 16.81 a ± 0.812 16.87 a ± 0.231 140.50 b ± 0.500 139.67 b ± 2.082<br />
S2x F0 46.87 d ± 1.848 45.17 g ± 0.764 8.07 e ± 0.115 8.05 e ± 0.777 52.33 f ± 2.517 55.00 g ± 2.000<br />
S2xF1 59.63 c ± 2.570 60.17 d ± 1.041 11.50 d ± 0.500 11.87 cd ± 0.777 74.00 d ± 3.606 79.93 e ± 1.675<br />
S2xF2 48.13 d ± 2.721 50.50 f ± 0.866 13.67 bc ± 0.577 13.87 b ± 0.325 74.67 d ± 1.528 83.33 e ± 2.082<br />
S2 xF3 49.67 d ± 1.528 51.17 f ± 1.041 10.87 d ± 0.231 10.90 d ± 0.361 70.00 e ± 1.000 68.33 f ± 1.155<br />
LSD at � 0.05 4.2170 1.7690 0.7569 1.3610 2.8090 3.7260<br />
Means with different letters within each column are significant at 0.05 level and means in the same column with the same letters are not significant. Mean ±Sd<br />
(standard deviation)<br />
Since: S = Soil salinity, i. e. S1 = 0.73 dsm -1 , S2 =4.95 dsm -1 ; F = Foliar spray with micronutrients, i. e. F0 = control, F1 = iron 250ppm, F2 = zinc 250ppm,<br />
F3= mixture <strong>of</strong> iron + zinc<br />
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Table 4. Effect <strong>of</strong> soil salinity, foliar spray with micronutruients and their interactions on plant height, branches number and herb fresh weight <strong>of</strong> Ocimum<br />
basilicum L. plants at first cut in 2006 and 2007 seasons.<br />
Treatments<br />
Dry weight g plant -1 Essential oil % Essential oil yield plant -1<br />
Season 1 Season 2 Season 1 Season 2 Season 1 Season 2<br />
S1 30.16 a ± 5.739 26.49 a ± 3.998 0.70 b ± 0.089 0.69 b ± 0.083 0.21 a ± 0.064 0.19 a ± 0.046<br />
S2 14.71 b ± 2.475 15.02 b ± 2.636 0.76 a ± 0.088 0.76 a ± 0.096 0.11 b ± 0.028 0.12 b ± 0.032<br />
LSD at � 0.05 2.0730 1.1370 0.0095 0.0123 0.0145 0.0034<br />
F0 16.63 d ± 6.445 16.30 c ± 6.123 0.60 d ± 0.043 0.59 c ± 0.033 0.10 d ± 0.033 0.10 d ± 0.033<br />
F1 22.02 c ± 6.580 19.90 b ± 4.769 0.72 c ± 0.039 0.74 b ± 0.037 0.16 c ± 0.042 0.15 c ± 0.034<br />
F2 24.67 b ± 9.694 22.85 a ± 6.791 0.76 b ± 0.048 0.75 b ± 0.064 0.18 b ± 0.062 0.17 b ± 0.039<br />
F3 26.42 a ± 11.314 23.97 a ± 7.731 0.83 a ± 0.037 0.82 a ± 0.041 0.21 a ± 0.085 0.19 a ± 0.054<br />
LSD at � 0.05 1.1730 1.2150 0.0325 0.0398 0.0080 0.0174<br />
S1xF0 22.47 d ± 0.896 21.83 d ± 1.258 0.57 ± 0.025 0.57 ± 0.027 0.13 de ± 0.003 0.12 de ± 0.013<br />
S1xF1 27.97 c ± 1.002 24.17 c ± 1.443 0.70 ± 0.040 0.72 ± 0.031 0.20 c ± 0.005 0.18 c ± 0.018<br />
S1xP2 33.50 b ± 0.500 28.97 b ± 1.704 0.72 ± 0.006 0.70 ± 0.000 0.24 b ± 0.006 0.20 b ± 0.012<br />
S1xF3 36.70 a ± 1.468 31.00 a ± 1.000 0.80 ± 0.021 0.78 ± 0.017 0.29 a ± 0.014 0.24 a ± 0.009<br />
S2x F0 10.80 f ± 0.985 10.77 f ± 0.580 0.63 ± 0.025 0.62 ± 0.021 0.07 f ± 0.007 0.07 f ± 0.004<br />
S2xF1 16.07 e ± 1.007 15.63 e ± 0.404 0.75 ± 0.025 0.75 ± 0.044 0.12 e ± 0.006 0.12 e ± 0.004<br />
S2xF2 15.83 e ± 0.764 16.73 e ± 0.404 0.80 ± 0.006 0.81 ± 0.042 0.13 de ± 0.006 0.13 de ± 0.010<br />
S2 xF3 16.13 e ± 0.709 16.93 e ± 0.058 0.85 ± 0.025 0.85 ± 0.017 0.14 d ± 0.002 0.14 d ± 0.004<br />
LSD at � 0.05 1.6580 1.7180 1.4920 0.7693 N.S N.S<br />
Means with different letters within each column are significant at 0.05 level and means in the same column with the same letters are not significant. Mean ±Sd<br />
(standard deviation)<br />
Since: S = Soil salinity, i. e. S1 = 0.73 dsm -1 , S2 =4.95 dsm -1 ; F = Foliar spray with micronutrients, i. e. F0 = control, F1 = iron 250ppm, F2 = zinc 250ppm,<br />
F3= mixture <strong>of</strong> iron + zinc<br />
105
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 5. Effect <strong>of</strong> soil salinity, foliar spray with micronutruients and their interactions on herb dry weight, essential oil % and essential oil yield <strong>of</strong> Ocimum<br />
basilicum L. plants at second cut in 2006 and 2007 seasons.<br />
Treatments<br />
Dry weight g plant -1 Essential oil % Essential oil yield plant -1<br />
Season 1 Season 2 Season 1 Season 2 Season 1 Season 2<br />
S1 40.49 a ± 3.288 39.68 a ± 3.623 0.66 b ± 0.083 0.66 b ± 0.075 0.27 a ± 0.051 0.26 a ± 0.050<br />
S2 21.40 b ± 2.424 21.39 b ± 2.220 0.73 a ± 0.083 0.73 a ± 0.080 0.16 b ± 0.030 0.16 b ± 0.030<br />
LSD at � 0.05 1.6190 3.1310 0.0393 0.0156 0.0231 0.0271<br />
F0 26.75 b ± 9.464 25.94 b ± 8.688 0.58 c ± 0.044 0.58 c ± 0.041 0.15 c ± 0.048 0.15 c ± 0.041<br />
F1 32.58 a ± 10.394 32.23 a ± 10.213 0.71 b ± 0.026 0.70 b ± 0.025 0.23 b ± 0.069 0.22 b ± 0.068<br />
F2 32.67 a ± 10.671 32.08 a ± 10.420 0.72 b ± 0.069 0.72 b ± 0.082 0.23 ab ± 0.055 0.22 b ± 0.050<br />
F3 31.78 a ± 11.570 31.87 a ± 10.905 0.78 a ± 0.038 0.77 a ± 0.039 0.25 a ± 0.080 0.24 a ± 0.073<br />
LSD at � 0.05 1.7420 0.8172 0.0303 0.0281 0.0164 0.0113<br />
S1xF0 35.33 ± 1.528 33.83 b ± 0.764 0.55 g ± 0.045 0.55 e ± 0.027 0.19 c ± 0.021 0.19 d ± 0.006<br />
S1xF1 42.00 ± 1.000 41.50 a ± 1.500 0.69 de ± 0.030 0.69 c ± 0.023 0.29 b ± 0.018 0.29 b ± 0.019<br />
S1xP2 42.33 ± 0.577 41.57 a ± 0.751 0.66 e ± 0.010 0.65 d ± 0.021 0.28 b ± 0.008 0.27 c ± 0.011<br />
S1xF3 42.30 ± 1.572 41.80 a ± 0.700 0.75 bc ± 0.031 0.74 b ± 0.017 0.32 a ± 0.016 0.31 a ± 0.012<br />
S2x F0 18.17 ± 0.764 18.04 d ± 1.066 0.61 f ± 0.006 0.62 d ± 0.015 0.11 e ± 0.005 0.11 f ± 0.007<br />
S2xF1 23.17 ± 1.756 22.97 c ± 0.950 0.72 cd ± 0.010 0.71 bc ± 0.023 0.17 d ± 0.012 0.16 e ± 0.009<br />
S2xF2 23.00 ± 2.000 22.60 c ± 1.039 0.78 ab ± 0.015 0.79 a ± 0.012 0.18 cd ± 0.015 0.18 de ± 0.010<br />
S2 xF3 21.27 ± 0.643 21.93 c ± 0.902 0.81 a ± 0.006 0.81 a ± 0.012 0.17 cd ± 0.004 0.18 de ± 0.010<br />
LSD at � 0.05 N.S 1.1560 0.0428 0.0398 0.0232 0.0159<br />
Means with different letters within each column are significant at 0.05 level and means in the same column with the same letters are not significant. Mean ±Sd<br />
(standard deviation)<br />
Since: S = Soil salinity, i. e. S1 = 0.73 dsm -1 , S2 = 4.95 dsm -1 ; F = Foliar spray with micronutrients, i. e. F0 = control, F1 = iron 250ppm, F2 = zinc 250ppm,<br />
F3= mixture <strong>of</strong> iron + zinc<br />
106
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 6. Effect <strong>of</strong> soil salinity and foliar spray with micronutruients on essential oil constituents <strong>of</strong> Ocimum basilicum L. plants<br />
in 2007 seasons.<br />
Soil salinity<br />
Compounds Saline soil (4.95 dsm )<br />
-1<br />
Normal soil (0.73 dsm )<br />
-1<br />
F0<br />
F1<br />
F2<br />
F3<br />
F0<br />
F1<br />
F2<br />
α–thujene--<br />
--<br />
--<br />
--<br />
--<br />
0.02<br />
0.01<br />
α-pinene<br />
0.42<br />
0.19<br />
0.32<br />
0.40<br />
0.29<br />
0.40<br />
0.01<br />
camphene--<br />
--<br />
--<br />
--<br />
--<br />
0.02<br />
0.46<br />
sabinene--<br />
--<br />
0.08<br />
0.07<br />
--<br />
0.01<br />
0.35<br />
β-pinene<br />
0.86<br />
0.94<br />
0.93<br />
1.21<br />
0.75<br />
1.18<br />
1.69<br />
myrcene--<br />
--<br />
--<br />
--<br />
0.45<br />
0.84<br />
1.33<br />
limonene<br />
0.37<br />
0.70<br />
0.76<br />
0.97<br />
0.64<br />
0.10<br />
0.11<br />
1 ,8-cineol 7.79<br />
9.40<br />
6.36<br />
7.99<br />
6.63<br />
8.39<br />
9.22<br />
α - terpinene 1.03<br />
0.93<br />
0.91<br />
0.93<br />
0.35<br />
0.10<br />
0.32<br />
ocimene--<br />
0.42<br />
0.36<br />
0.36<br />
0.48<br />
0.12<br />
0.41<br />
Linalool<br />
39.85<br />
32.42<br />
27.68<br />
25.68<br />
38.28<br />
46.54<br />
49.33<br />
camphor--<br />
--<br />
0.27<br />
0.06<br />
0.02<br />
0.22<br />
0.29<br />
1,4-terpineol 1.05<br />
1.34<br />
0.78<br />
0.73<br />
1.70<br />
0.66<br />
0.89<br />
methylchavicol 35.64<br />
30.84<br />
44.01<br />
38.52<br />
21.48<br />
27.67<br />
23.66<br />
nerol<br />
1.00<br />
1.89<br />
1.29<br />
1.11<br />
0.89<br />
1.22<br />
1.09<br />
geroniol<br />
0.75<br />
1.23<br />
1.13<br />
1.18<br />
2.02<br />
0.85<br />
0.59<br />
eugenol--<br />
--<br />
--<br />
--<br />
--<br />
--<br />
--<br />
caryophyllene-- 0.44<br />
0.24<br />
0.37<br />
0.18<br />
0.12<br />
0.01<br />
germacrene D 2.19<br />
3.89<br />
1.80<br />
2.88<br />
2.32<br />
4.38<br />
4.08<br />
cadinene--<br />
0.09<br />
--<br />
0.10<br />
0.11<br />
--<br />
--<br />
cis-bisabolene 1.71<br />
1.98<br />
1.74<br />
2.04<br />
2.53<br />
--<br />
--<br />
nerolidole<br />
0.08<br />
0.41<br />
0.60<br />
0.25<br />
0.44<br />
0.43<br />
0.45<br />
selinene<br />
0.42<br />
0.60<br />
0.05<br />
0.86<br />
0.01<br />
0.09<br />
0.74<br />
t-cadinol<br />
3.25<br />
3.91<br />
4.02<br />
4.76<br />
--<br />
1.38<br />
1.61<br />
Identified<br />
compounds<br />
96.31<br />
91.62<br />
93.33<br />
90.47<br />
91.42<br />
99.26<br />
93.13<br />
F = Foliar spray with micronutrients, i. e. F0 = control, F1 = iron 250ppm, F2 = zinc 250ppm, F3 = mixture <strong>of</strong> iron + zinc<br />
107<br />
F3<br />
--<br />
--<br />
--<br />
0.47<br />
0.30<br />
0.05<br />
0.01<br />
6.04<br />
0.31<br />
0.40<br />
52.14<br />
0.14<br />
0.78<br />
20.34<br />
1.78<br />
1.07<br />
0.42<br />
--<br />
3.63<br />
--<br />
--<br />
0.30<br />
0.91<br />
1.75<br />
91.35
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
CONCLUSIONS<br />
It may be concluded that Ocimum basilicum (linalool and methylchavicol chemo type) is tolerant to<br />
soil salinity, thus we may recommend its cultivation in slain soil <strong>of</strong> Egypt. Foliar spraying with iron<br />
and /or zinc under these conditions could be much more efficient than not application <strong>of</strong> nutrients. So,<br />
we recommended that, foliar application <strong>of</strong> iron and /or zinc to raise the salt stress tolerance <strong>of</strong> sweet<br />
basil (Ocimum basilicum L.).<br />
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111
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Growth and yield <strong>of</strong> Foeniculum vulgare var.azoricum as influenced by some<br />
vitamins and amino acids<br />
S.F. Hendawy and Azza A.Ezz El-Din*<br />
Cultivation and Production <strong>of</strong> Medicinal and Aromatic Plants Dept.<br />
National Research Centre, Dokki, Cairo -12622, Egypt<br />
E-mail address for correspondence :azzaamin2001@hotmail.com<br />
___________________________________________________________________________________<br />
Abstract :This investigation was carried out in Saft El-Laban farm, Giza during two successive<br />
seasons <strong>of</strong> 2006/2007 and 2007/2008 to study the effect <strong>of</strong> foliar application <strong>of</strong> ascorbic acid and<br />
thiamine in a rate <strong>of</strong> 0, 25 , 50 and 75 mgL -1 . for each as well as amino acids i.e aspartic and phenyl<br />
alanin in a rate <strong>of</strong> 0, 100, 200 and 300 ppm for each on growth, yield and chemical composition <strong>of</strong><br />
fennel plants. The obtained results could be summarized as follows: ascorbic acid at 75 mgL -1 .<br />
recorded the best value <strong>of</strong> plant height, number <strong>of</strong> branches, number <strong>of</strong> flower heads and seed weight<br />
per plant. No significant difference was shown between aspartic acid and ascorbic acid. Phenyl alanin<br />
at 300 ppm resulted the highest essential oil percent (2.78%) compared with control (2.00%).<br />
Key words: Foeniculum vulgare, ascorbic acid, aspartic, phenylalanine, thiamine, essential oil<br />
__________________________________________________________________________________<br />
INTRODUCTION<br />
Foeniculum vulgare (Fennel) belonging to the family Apiaceae is a perennial herb native to the<br />
Mediterranean Region. It is widely cultivated and extensively used as a culinary spice. The plant is<br />
aromatic and is used as a pot herb. The leaves have diuretic properties and the roots are regarded as<br />
purgatives. Dried fruits <strong>of</strong> fennel posses a pleasant aromatic taste and used for flavouring soups, meat<br />
dishes and sauces. The fruits are considered to be usefull in treatment <strong>of</strong> diseases <strong>of</strong> the chest, spleen<br />
and kidney (Singh and Kale 2008).<br />
The anti-inflammatory, analgesic and antioxidant activities <strong>of</strong> the fruits <strong>of</strong> fennel have been reported by<br />
(Choi and Hwang 2004).<br />
The oil <strong>of</strong> fennel regulates the peristaltic functions <strong>of</strong> the gastrointestinal tract and relevies the spasms<br />
<strong>of</strong> intestines (Fathy et al 2002).<br />
Amino acids are fundamental ingredients in the process <strong>of</strong> protein synthesis. Glycine and Glutamic<br />
acids play an important role in formation <strong>of</strong> vegetative tissue and chlorophyll. They also have a<br />
chelating effect on micronutrients through making their absorption and transportation easier for the<br />
plant. They are precursors or activators <strong>of</strong> phytohormones and growth substances. L. Methionine is a<br />
precursor <strong>of</strong> ethylene and growth factors such as espermine and espermidine (Singh 1999).<br />
Gamal El-Din et al (1997) found that foliar application <strong>of</strong> ornithine and phenylalanine 50, 100 mgL -1 .<br />
on Cymbopgon citrates led to significantly increase in vegetative growth, number <strong>of</strong> leaves and tillers<br />
as well as fresh and dry weight <strong>of</strong> herb. El-Sherbeny and Hassan (1987) reported that phenylalanine<br />
or tryptophan at 200 or 250 mgL -1 significantly increased growth parameters and alkaloid content <strong>of</strong><br />
datura plants.<br />
Moursy et al (1988) indicated that phenylalanine or ornithine increased the fresh and dry weight <strong>of</strong><br />
callus explants <strong>of</strong> Datura stramonium L. Refaat and Naguib (1998) found that spraying peppermint<br />
plant with alpha-alanine at 25 and 50 ppm increased fresh and dry weight <strong>of</strong> the plant and essential oil<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
content. Harridy (1986) mentioned that the higher alkaloid percentage and yield <strong>of</strong> Catharanthus<br />
roseus resulted from foliar application <strong>of</strong> some amino acids. Similar trend was observed by Awad<br />
(1986), studying methionen on Hyoscyamus muticus. Talaat and Youssef (2002) found a pronounced<br />
increase in vegetative growth <strong>of</strong> basil plant as a result <strong>of</strong> lysine and ornithine treatments.<br />
Little information are available about the role <strong>of</strong> vitamins in regulating the biosynthesis <strong>of</strong> essential oil<br />
in plants. Robinson (1973) reported that vitamin B complex and vitamin C act as co-enzmes in the<br />
enzymatic reactions by which carbohydrates, fats and proteins are metabolized and involved in<br />
photosynthesis and respiration. Taraf et al (1999) reported that foliar application <strong>of</strong> nicotine amide to<br />
lemongrass plants significantly promoted vegetative growth as well as essential oil percent, oil yield<br />
per plant, total carbohydrates and crude proteins.<br />
Ascorbic acid (vitamin C) is known as a growth regulating factor which influences many biological<br />
processes. Price (1966) reported that ascorbic acid (vit.C) increases nucleic acid content, especially<br />
RNA. It also influenced the synthesis <strong>of</strong> enzymes, nucleic acids and protein, in addition it acts as coenzyme<br />
in metabolic changes. Abd El-Halim (1995) reported that foliar application <strong>of</strong> ascorbic acid on<br />
tomato plants significantly increased growth parameters (stem length, number <strong>of</strong> branches, leaves,<br />
flowers and fruit set as well as dry weight <strong>of</strong> shoot per plant) in comparison with control plants.<br />
Thiamine (Vitamin B1) is a necessary ingredient for biosynthesis <strong>of</strong> the coenzyme thiamine<br />
pyrophosphate, in this latter form it plays an important role in carbohydrate metabolism. It is an<br />
essential nutrient for both plant and animal. In plants, it is synthesized in the leaves and is transported<br />
to the roots where it controls growth. Thiamine is an important c<strong>of</strong>actor for the transketolation reaction<br />
<strong>of</strong> the pentose phosphate for nucleotide synthesis and for the reduced NADP required for various<br />
synthetic pathways. It acts as co-enzyme oxidative carboxylation <strong>of</strong> � -keto acids (e.g. � ketoglutarate,<br />
pyruvate, the � -keto analogs <strong>of</strong> the branched-chain amino acids: leucine isoleucine and<br />
valine) Kawasaki (1992). In this concern, Reda et al (1977) reported that thiamine treatment<br />
significantly increased the total yield <strong>of</strong> chromones as well as khellin and visnagin yield (mg plant -1 ) in<br />
the fruits <strong>of</strong> Ammi visnaga. Ascorbic acid seemed to retard the growth <strong>of</strong> Ammi Visnaga but the yield<br />
<strong>of</strong> different chromones in the fruits under the effect <strong>of</strong> ascorbic acid (50 and 100 mg/1) was about three<br />
folds that <strong>of</strong> the corresponding control.<br />
The aim <strong>of</strong> this study is to investigate the effect <strong>of</strong> some vitamins and amino acids on growth, yield and<br />
oil composition <strong>of</strong> fennel plants.<br />
Field experiments:<br />
MATERIALS AND METHODS<br />
Field experiments were carried out at Saft El-Laban farm, Giza, Egypt during two successive growing<br />
seasons (2007 and 2008) to study foliar application <strong>of</strong> some vitamins i.e ascorbic acid and thiamine and<br />
amino acids i.e aspartic and phenylalanine on growth, yield and chemical composition <strong>of</strong> fennel plants.<br />
Seeds <strong>of</strong> Foeniculum vulgare var. azoricum were obtained from Sekem Group Company, Egypt.<br />
The mechanical and chemical analysis <strong>of</strong> the soil were carried out according to the method <strong>of</strong><br />
Chapman and Pratt (1978), which were presented in Table (1).<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table (1): Physical and chemical analysis <strong>of</strong> the experimental soil.<br />
Physical properties Chemical parameters<br />
Soil type loamy<br />
Course sand 4.9%<br />
Fine sand 30.7%<br />
Silt 27.5%<br />
Clay 27.5%<br />
Organic matter 2.1%<br />
115<br />
pH<br />
Available N<br />
Available P2O5<br />
Available K2O<br />
Fe<br />
Mn<br />
Zn<br />
Cu<br />
Na<br />
Mg<br />
7.8<br />
13.8 mg/100g<br />
0.482 mg/100g<br />
3.01 mg/100g<br />
1.1 ppm<br />
0.53 ppm<br />
21 ppm<br />
21 ppm<br />
29 ppm<br />
2.4 ppm<br />
Seeds were sown directly in soil on 12 th <strong>of</strong> October 2006, and on the 2 nd <strong>of</strong> October 2007. The<br />
experimental unit area was 4 m 2 and the treatments were arranged in completely randomized block<br />
design with three replicates for each treatment. Each plot contained 3 rows <strong>of</strong> 60 cm apart and the<br />
distance between plants was 30 cm. Calcium super phosphate (15.5% P2O5), at 100 kg/ feddan,<br />
ammonium sulphate (20.5%N) at 150 kg/ feddan and potassium sulphate (48% K2O) at 100kg/feddan<br />
were applied. Phosphorus fertilizer was added at the time <strong>of</strong> soil preparation while nitrogen fertilizer<br />
was added at two separated side dressings, the first one on 15 th. December and the second on 15 th.<br />
February in both seasons.<br />
The treatments were as follows:<br />
Treat. 1: Control (Sprayed with water)<br />
Treat.2: Sprayed with aspartic acid at 100 ppm.<br />
Treat.3: Sprayed with aspartic acid at 200 ppm.<br />
Treat.4: Sprayed with aspartic acid at 300 ppm.<br />
Treat.5: Sprayed with Phenyl alanin at 100 ppm.<br />
Treat.6: Sprayed with Phenyl alanin at 200 ppm..<br />
Treat.7: Sprayed with Phenyl alanin at 300 ppm.<br />
Treat.8: Sprayed with thiamine at 25 mg/L.<br />
Treat.9: Sprayed with thiamine at 50 mg/L.<br />
Treat.10:Sprayed with thiamine at 75 mg/L.<br />
Treat.11:Sprayed with ascorbic acid at 25 mg/L.<br />
Treat.12:Sprayed with ascorbic acid at 50 mg/L.<br />
Treat.13:Sprayed with ascorbic acid at 75 mg/L.<br />
The plants were sprayed with vitamins or amino acids twice, the first one on 15 th December and the<br />
second on 15 th February, early in the morning, while the control plants were sprayed with distilled<br />
water.<br />
Plant height (cm), plant fresh weight or (aerial parts)g plant -1 plant dry weight (aerial parts), g plant-1<br />
flowers head number, no <strong>of</strong> branches, no. <strong>of</strong> suckers and seed weight per plant were recorded through<br />
the two growth seasons. Essential oil percentage was determined in the fruits.
Chemical analysis:<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Samples <strong>of</strong> dried seeds were subjected to water distillation for determination <strong>of</strong> their essential oil<br />
content using clevenger's apparatus Marotti and Piccaglia (1992).<br />
Oil samples were subjected to Gas Chromatographic Analysis to identify their oil composition adopting<br />
the following condition:<br />
Apparatus: Thermo Quest Trace GC 2000 Series-Finnegan<br />
Standard material: Piano paraffines SUPELCO product.<br />
Column: 60m x 0.32 mm SPB TM -5<br />
Detector: FID; Operating mode Splitless; Base temp. 300 o C<br />
Mobile phase: Nitrogen 30ml/min<br />
Oven Program: Initial temp. 40 o C, rate <strong>of</strong> increase 3 o C/minute; Final temp. 240 o C; Hold time 10<br />
minutes.<br />
The results <strong>of</strong> all the parameters were statistically analysed adopted the method <strong>of</strong> (Snedecor and<br />
Cochran 1980).<br />
RESULTS AND DISCUSSION<br />
Table (2&3) showed the effect <strong>of</strong> foliar application <strong>of</strong> vitamins i.e, ascorbic acid (vitamin C) and<br />
thiamine (vitamin B1) as well as amino acids i.e, aspartic acid and phenylalanine on growth and yield<br />
<strong>of</strong> Foeniculum vulgare var. azoricum during 2007 and 2008. The data indicate that application <strong>of</strong><br />
aspartic acid increased plant height (cm) up to<br />
116
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table(2): Effect <strong>of</strong> foliar application <strong>of</strong> ascorbic acid and thiamine and amino acids, aspartic and phenylalanine on growth, yield and chemical composition<br />
Foeniculum vulgare var. azoricum plants; First season (2007).<br />
Treatments<br />
Plant height<br />
(cm)<br />
Aerial parts<br />
fresh weight<br />
g plant -1<br />
Aerial parts<br />
dry weight<br />
g plant -1<br />
117<br />
Number <strong>of</strong><br />
flower heads<br />
plant -1<br />
Number <strong>of</strong><br />
branches<br />
plant -1<br />
Number <strong>of</strong><br />
suckers plant -1<br />
Seed weight<br />
g plant -1<br />
Control 0ppm 128.0 650.0 98.48 30.0 8.0 2.0 38.0 2.00<br />
Aspartic<br />
Phenylalanine<br />
Thiamine<br />
Ascorbic acid<br />
100 ppm<br />
200 ppm<br />
300 ppm<br />
Mean<br />
L.S.D. (5%)<br />
100 ppm<br />
200 ppm<br />
300 ppm<br />
Mean<br />
L.S.D. (5%)<br />
25 mg L -1<br />
50 mg L -1<br />
75 mg L -1<br />
Mean<br />
L.S.D. (5%)<br />
25 mg L -1<br />
50 mg L -1<br />
75 mg L -1<br />
Mean<br />
L.S.D. (5%)<br />
158.0<br />
173.0<br />
178.0<br />
169.7<br />
5.12<br />
145.0<br />
155.0<br />
158.0<br />
152.7<br />
4.60<br />
167.0<br />
185.0<br />
184.0.<br />
178.7<br />
5.90<br />
170.0<br />
194.0<br />
185.0<br />
183.0<br />
6.33<br />
710.0<br />
745.0<br />
768.0<br />
741.0<br />
28.16<br />
705.0<br />
715.0<br />
734.0<br />
718.0<br />
24.16<br />
714.0<br />
735.0<br />
772.0<br />
740.3<br />
27.00<br />
766.0<br />
780.0<br />
790.0<br />
778.7<br />
23.51<br />
107.58<br />
112.88<br />
116.36<br />
112.3<br />
2.94<br />
110.16<br />
111.72<br />
114.69<br />
112.2<br />
N.S.<br />
105.00<br />
108.09<br />
113.53<br />
108.9<br />
3.10<br />
117.85<br />
120.00<br />
121.54<br />
119.8<br />
2.80<br />
L.S.D. (5%) for foliar appli. 6.12 21.60 2.34 2.18 0.90 0.36 2.85 0.074<br />
38.0<br />
42.0<br />
48.0<br />
42.7<br />
2.41<br />
35.0<br />
39.0<br />
42.0<br />
38.7<br />
2.38<br />
35.0<br />
42.0<br />
48.0<br />
41.7<br />
2.21<br />
38.0<br />
45.0<br />
50.0<br />
44.3<br />
2.26<br />
10.0<br />
12.0<br />
12.0<br />
11.3<br />
0.90<br />
12.0<br />
14.0<br />
15.0<br />
13.7<br />
1.10<br />
10.0<br />
12.0<br />
13.0<br />
11.7<br />
0.80<br />
11.0<br />
13.0<br />
15.5<br />
13.0<br />
1.11<br />
3.0<br />
3.0<br />
5.0<br />
3.7<br />
0.40<br />
3.0<br />
4.0<br />
4.0<br />
3.7<br />
N.S.<br />
4.0<br />
5.0<br />
5.0<br />
4.7<br />
0.35<br />
4.0<br />
6.0<br />
6.0<br />
5.3<br />
0.38<br />
45.0<br />
49.0<br />
52.0<br />
48.7<br />
2.34<br />
40.0<br />
45.0<br />
48.0<br />
44.3<br />
2.47<br />
48.0<br />
55.0<br />
58.0<br />
53.7<br />
2.35<br />
52.0<br />
58.0<br />
61.0<br />
57.0<br />
2.71<br />
Oil%<br />
2.20<br />
2.32<br />
2.45<br />
2.3<br />
0.090<br />
2.43<br />
2.51<br />
2.58<br />
2.5<br />
0.092<br />
2.44<br />
2.48<br />
2.53<br />
2.5<br />
0.075<br />
2.48<br />
2.55<br />
2.67<br />
2.6<br />
0.070
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table(3). Effect <strong>of</strong> foliar application <strong>of</strong> ascorbic acid and thiamine and amino acids, aspartic and phenylalanine on growth, yield and chemical composition<br />
Foeniculum vulgare var. azoricum plants; Second season (2008).<br />
Treatments<br />
Plant height<br />
(cm)<br />
Aerial parts<br />
fresh weight<br />
g plant -1<br />
Aerial parts<br />
dry weight<br />
g plant -1<br />
118<br />
Number <strong>of</strong><br />
flower heads<br />
plant -1<br />
Number <strong>of</strong><br />
branches<br />
plant -1<br />
Number <strong>of</strong><br />
suckers plant -1<br />
Seed weight<br />
g plant -1<br />
Control 0ppm 132.0 675.0 102.27 30.0 9.0 3.0 37.0 2.00<br />
Aspartic<br />
Phenylalanine<br />
Thiamin<br />
Ascorbic acid<br />
100 ppm<br />
200 ppm<br />
300 ppm<br />
Mean<br />
L.S.D. (5%)<br />
100 ppm<br />
200 ppm<br />
300 ppm<br />
Mean<br />
L.S.D. (5%)<br />
25 mg L -1<br />
50 mg L -1<br />
75 mg L -1<br />
Mean<br />
L.S.D. (5%)<br />
25 mg L -1<br />
50 mg L -1<br />
75 mg L -1<br />
Mean<br />
L.S.D. (5%)<br />
155.0<br />
170.0<br />
174.0<br />
166.3<br />
5.05<br />
148.0<br />
156.0<br />
160.0<br />
154.7<br />
4.63<br />
165.0<br />
182.0<br />
189.0<br />
178.7<br />
5.82<br />
170.0<br />
194.0<br />
185.0<br />
183.0<br />
6.12<br />
714.0<br />
733.0<br />
756.0<br />
734.3<br />
26.00<br />
724.0<br />
733.0<br />
754.0<br />
737.0<br />
21.32<br />
722.0<br />
730.0<br />
775.0<br />
742.3<br />
25.14<br />
755.0<br />
784.0<br />
788.0<br />
775.7<br />
23.51<br />
108.18<br />
111.06<br />
114.55<br />
111.3<br />
2.88<br />
113.13<br />
114.53<br />
117.81<br />
115.2<br />
2.56<br />
106.18<br />
107.35<br />
113.97<br />
109.2<br />
2.94<br />
116.15<br />
120.62<br />
121.23<br />
119.3<br />
2.14<br />
L.S.D. (5%) for foliar appli. 6.08 22.30 2.55 2.01 0.85 0.24 2.78 0.078<br />
36.0<br />
43.0<br />
48.0<br />
42.3<br />
2.11<br />
36.0<br />
41.0<br />
45.0<br />
40.7<br />
2.08<br />
37.0<br />
44.0<br />
49.0<br />
43.3<br />
2.03<br />
38.0<br />
48.0<br />
52.0<br />
46.0<br />
2.06<br />
10.0<br />
13.0<br />
14.0<br />
12.3<br />
0.75<br />
13.0<br />
14.0<br />
15.0<br />
14.0<br />
0.84<br />
13.0<br />
14.0<br />
14.0<br />
13.7<br />
0.70<br />
12.0<br />
15.0<br />
15.0<br />
14.0<br />
0.90<br />
3.0<br />
5.0<br />
5.0<br />
4.3<br />
N.S.<br />
4.0<br />
5.0<br />
6.0<br />
5.0<br />
N.S.<br />
4.0<br />
6.0<br />
6.0<br />
5.3<br />
0.25<br />
5.0<br />
6.0<br />
7.0<br />
6.0<br />
0.22<br />
43.0<br />
49.0<br />
53.0<br />
48.3<br />
2.28<br />
42.0<br />
47.0<br />
50.0<br />
46.3<br />
2.40<br />
48.0<br />
53.0<br />
57.0<br />
52.7<br />
2.25<br />
54.0<br />
60.0<br />
63.0<br />
59.0<br />
2.65<br />
Oil%<br />
2.20<br />
2.35<br />
2.40<br />
2.3<br />
0.095<br />
2.41<br />
2.48<br />
2.78<br />
2.5<br />
0.084<br />
2.48<br />
2.51<br />
2.58<br />
2.5<br />
0.086<br />
2.47<br />
2.53<br />
2.64<br />
2.5<br />
0.071
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
300 ppm, but this increment had no significant effect comparing with 200 ppm. The maximum value <strong>of</strong><br />
this character was obtained by applying ascorbic acid at the rate <strong>of</strong> 50 mgL -1 . This was true during both<br />
seasons except thiamine and ascorbic acid in the second one, whereas the three applied doses were<br />
significant up to 75 mgL -1 . Wahba et al 2002 reported that aspartic acid as foliar spray (25, 50 and 75<br />
ppm) increased the vegetative growth, flowering parameters and yield <strong>of</strong> courms <strong>of</strong> Anthoglyza<br />
aethiopica.<br />
Fresh and dry weight <strong>of</strong> aerial parts significantly increased by increasing all treatments up to 300 ppm<br />
for asp. and phenyl. and 75 mg for vit. B1 and vit. C during the 1 st . season. In the 2 nd . season, the higher<br />
dose applied from vitamins and amino acids, the maximum fresh and dry weight more obtained. The<br />
highest weights were recorded with spraying ascorbic acid at 75 mgL -1 . Gamal El-Din and Abd El-<br />
Wahed (2005) stated that all amino acids treatments (ornithine, proline and phenlyalanin) significantly<br />
increased plant height, number <strong>of</strong> branches, number <strong>of</strong> flower heads and fresh and dry weights <strong>of</strong> aerial<br />
part <strong>of</strong> chamomile plant.<br />
Applying ascorbic acid significantly increased number <strong>of</strong> flower heads in fennel plants up to the higher<br />
dose. The same effect was observed when spraying aspartic acid, phenylalanine and thiamine.<br />
Ascorbic acid is not only an important antioxidant, it also appears to link flowering time,<br />
developmental senescence, programmed cell death and responses to pathogens (Pastori et al 2003;<br />
Barth et al 2004 and Pavet et al 2005). Furthermore, it affects nutritional cycle's activity in higher<br />
plants and plays an important role in the electron transport system Liu et al (1997). El-Banna et al<br />
(2006) found stimulatory effects <strong>of</strong> vitamin C on potato. Golan-Goldhirsh et al (1995) indicated that<br />
soybean treated with ascorbic acid increased photosynthesis process. Talaat (2003) detected that<br />
ascorbic foliar application on sweet paper increased content <strong>of</strong> macro-nutrients (N, P and K).<br />
Increasing aspartic acid doses significantly increased seed weight g plant -1 up to 300 ppm. Spraying<br />
vitamin C at 75 mgL -1 . resulted in the maximum seed weight. Attoa et al (2002) found that aspartic<br />
acid at 75 ppm increased both the fixed oil and total glucosinolate contents <strong>of</strong> Iberis amara. The<br />
maximum oil % was achieved from 300 ppm <strong>of</strong> phenylalanine (2.78%) compared with control (2.00%).<br />
Table (4) showed the effect <strong>of</strong> foliar application <strong>of</strong> ascorbic acid and thiamine and amino acids,<br />
aspartic and phenylalanine on essential oil composition <strong>of</strong> Foeniculum vulgare var. azoricum. The<br />
analysis <strong>of</strong> essential oil <strong>of</strong> fennel showed the presence <strong>of</strong> 7 componds as main constituents. The major<br />
one was found to be anethol (trans-1- methoxy-4- (Prop-1- enly) benzene; C10H12O).<br />
It ranged from 61.55 to 77.31%, followed by fenchone with values <strong>of</strong> 6.14 to 13.62%. Estragol<br />
occupied the third place and recorded 4.21% to 9.54%. Braun and Franz (1999) found that anethole,<br />
estragole, fenchone and Limonene are the major constituents <strong>of</strong> fennel essential oil. They represent<br />
99% <strong>of</strong> herb oil and 93% <strong>of</strong> the fruits oil. Mahfouz and Sharaf El-Din (2007) reported that Anethole<br />
was the main component in F.vulgare oil. It reached the highest value with half dose <strong>of</strong> N, P and K<br />
(mineral fertilization 357 kg ammonium sulphate + 238 kg calcium super-phosphate +60 kg potassium<br />
sulphate ha -1 ) and inoculation with Basillus megatherium).<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table(4). Effect <strong>of</strong> foliar application <strong>of</strong> ascorbic acid and thiamine and amino acids, aspartic and phenylalanine on oil composition <strong>of</strong> Foeniculum vulgare var. azoricum .<br />
Treatments � -pinene � -pinene Myrcene Limonene Fenchone Estragol Anethol Un-Known<br />
Total identified<br />
compounds<br />
Control 0 2.24 0.44 1.55 7.33 10.24 9.54 61.55 7.11 92.89<br />
Aspartic 100 ppm 1.15 traces 2.11 6.54 9.15 8.71 62.14 10.2 89.8<br />
200 ppm 1.36 0.16 0.06 6.65 9.13 8.82 64.21 9.61 90.39<br />
300 ppm 1.34 0.21 0.18 7.02 9.24 7.16 65.02 9.83 90.17<br />
Phenylalanine 100 ppm 1.44 0.33 0.16 9.14 10.38 6.23 62.34 9.98 90.02<br />
200 ppm 1.45 0.25 0.95 7.25 12.45 6.31 68.11 3.23 96.77<br />
300 ppm 1.48 0.24 0.38 7.93 12.36 6.01 68.42 3.76 96.24<br />
Thiamine 25 mg L -1<br />
50 mg L -1<br />
75 mg L -1<br />
1.01 0.29 0.36 6.54 10.14 6.42 64.32 9.53 90.47<br />
1.06 0.41 0.41 6.72 11.21 6.13 65.16 9.08 90.92<br />
1.18 0.45 0.45 6.72 10.25 6.02 66.17 8.76 91.24<br />
Ascorbic 25 mg L -1<br />
50 mg L -1<br />
75 mg L -1<br />
1.32 0.38 0.85 5.13 13.62 4.32 72.22 2.16 97.84<br />
1.35 0.36 0.93 5.14 6.14 4.21 77.31 4.56 95.44<br />
1.38 0.25 0.99 5.16 8.36 4.45 74.16 5.25 94.75<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Khalil et al (2008) stated that the major components in fennel seed oil are anethole, more than 45%<br />
and limonene, more than 12%. Abd El-Wahab and Mehasen (2009) reported that anethole content<br />
recorded higher percentage in Indian fennel than local fennel in all sowing time (7, 15 and 21 Nov. )<br />
and sowing locations (El-Minia, Assuit, Sohag and Qena governorates) under upper Egypt conditions.<br />
CONCLUSION<br />
We recommended that among all applied treatments, ascorbic acid at 75 mg L -1 resulted in the best<br />
values <strong>of</strong> growth parameters, while phenylalanine at concentration <strong>of</strong> 300 ppm recorded the highest<br />
essential oil percent compared with control.<br />
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Fathy, M.S., Shehata, A.H, Kaleel, A.E, Ezzat, S.M., 2002. An acylated Kaempferol glycoside from<br />
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Gamal El-Din, K.M., Abd El-Wahed, M.S.A., 2005. Effect <strong>of</strong> some amino scids on growth and<br />
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Gamal El-Din, K.M., Tarraf, S.A., Balbaa, L.K., 1997. Physiological studies on the effect <strong>of</strong> some<br />
amino acids and microelements on growth and essential oil content in lemongrass<br />
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Golan-Goldhirsh, A., Mozafar, A., Oerti, J.J., 1995. Effect <strong>of</strong> ascorbic acid on soybean seedlings grown<br />
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Harridy, I.M.A., 1986. Physiological studies on periwinkle plant (Catharanthus roseus G. Don). Ph.D<br />
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Inc., New York, U.S.A., pp. 319-354.<br />
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essential oil content <strong>of</strong> fennel (Foeniculum vulgare Mill). Int. Agrophysics, 21, 361-366.<br />
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<strong>of</strong> three varieties <strong>of</strong> Foeniculum vulgare Mill. J. <strong>of</strong> Essential Oil Res. 4, 569-576.<br />
Moursy, H.A. L., Hussein, M.S., El-Bahr., K.M., 1988. Effect <strong>of</strong> some alkaloid precursors on the<br />
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Pastori, G.M., Kiddle, G., Antoniw, J., Bernard, S., Veljovic – Jovanovic, S., Verrier, P.J., Noctor, G.,<br />
Foyer, C.H., 2003. Leaf vitamin C contents modulate plant defense development through<br />
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Pavet, V., Olmos, E., Kiddle, G., Mowla, S., Kumar, S., Antoniw, J., Alvarez, M.E., Foyer, C.H., 2005.<br />
Ascorbic acid deficiency activates cell death and disease resistance responses in Arabidopsis.<br />
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The effect <strong>of</strong> thiamine and ascorbic acid on growth and chromone yield. Egypt. J. Pharm. Sci.,<br />
18, 19-27.<br />
Refaat, A.M., Naguib, Y.N, 1998. Peppermint yields and oil quality as affected by application <strong>of</strong> some<br />
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Robinson, F.A., 1973. Vitamins. In Phytochemistry. Vol. III: 195-220. Lawrence, Miller, P., (ed) Van-<br />
Nostrand Reinhold Co., New York.<br />
Singh, B., Kale, R.K., 2008. Chemomodulatory action <strong>of</strong> Foeniculum vulgare (fennel) on skin and<br />
forestomach papillomagenesis, enzymes associated with xenobiotic metabolism and<br />
antioxidant status in murine model system. Food and Chem.. Toxi., 46, 3842-3850.<br />
Singh, B.K., 1999. Plant Amino Acids: Biochemistry and Biotechnology. Marcel Dekker Inc., New<br />
York, U.S.A, pp.648.<br />
Snedecor, G.W., Cochran, W.C., 1980. Statistical methods' 7 th Ed., Iowa State Univ., Ames, Iowa,<br />
U.S.A., pp. 507.<br />
Talaat, I.M., Yussef, A.A., 2002. The role <strong>of</strong> the amino acids lysine and ornithine in growth and<br />
chemical constituents <strong>of</strong> Basil plant. Egypt. J. Appl. Sci, 17, 83-95.<br />
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Talaat, N.B., 2003. Physiological studies on the effect <strong>of</strong> salinity, ascorbic acid and putrescine <strong>of</strong> sweet<br />
paper plant. Ph.D Thesis, Fac. <strong>of</strong> Agric., Cairo Univ.<br />
Taraf, S.A., Gamal El-Din, K.M., Balbaa, L.K., 1999. The response <strong>of</strong> vegetative growth and essential<br />
oil <strong>of</strong> lemongrass (Cymbopogon citrates Hort) to foliar application <strong>of</strong> ascorbic acid,<br />
nicotinamid and some micronutrients. Arab Univ. <strong>of</strong> Agric. Sci., 7, 247-259.<br />
Wahba, H., Mohamed, S.M., Attoa, G.E., Farahat, A.A., 2002. Response <strong>of</strong> Antholyza aethiopica to<br />
foliar spray with some amino acids and mineral nutrition with sulphur. Annals Agric. Sci., Ain<br />
Shams Univ., 47, 929-944.<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Effect <strong>of</strong> water stress and potassium humate on the productivity <strong>of</strong> oregano plant<br />
using saline and fresh water irrigation<br />
H.A.H. Said-Al Ahl* and M.S. Hussein<br />
Department <strong>of</strong> Cultivation and Production <strong>of</strong> Medicinal and Aromatic Plants,<br />
National Research Centre, Dokki, Giza, Egypt.<br />
Postal code: 12622<br />
*E-mail address for correspondence: saidalahl@yahoo.com<br />
_________________________________________________________________________________<br />
Abstract: To study the response <strong>of</strong> oregano (Origanum vulgare L.) plants to soil moisture regimes<br />
using fresh and saline water irrigation and potassium humate fertilization, a pot experiment was<br />
conducted during two successive seasons (2007/2008 and 2008/2009) under the natural conditions <strong>of</strong><br />
the greenhouse <strong>of</strong> the National Research Center, Dokki, Giza, Egypt. Herb fresh weight g plant -1 and<br />
the content and yield ml plant -1 <strong>of</strong> essential oil were decreased significantly by using saline water<br />
irrigation compared to fresh water irrigation. Herb fresh weight g plant -1 and essential oil yield ml<br />
plant -1 <strong>of</strong> Origanum vulgare L were significantly decreased with the rise in water stress levels.<br />
Whereas, there was significant increase in essential oil % by using lower level <strong>of</strong> available soil<br />
moisture (30% ASM) followed by 90% ASM and then 60% ASM contained the highest values <strong>of</strong><br />
essential oil %. Fresh herb and essential oil production increased significantly with K-humate<br />
application. The maximum <strong>of</strong> herb fresh and essential oil yields were obtained from plants irrigated<br />
with 90% available soil moisture fresh water combined with k-humate fertilizer 1.5 g pot -1 . Essential<br />
oil % recorded their maximum value from plants irrigated with 60% ASM fresh water combined with<br />
1.5 g pot -1 K-hum ate. Totally, 20 compounds were identified in essential oils <strong>of</strong> three populations by<br />
means <strong>of</strong> GLC. Carvacrol was the dominant compound (46.44–77.96%) for all essential oil samples,<br />
followed by p-cymene (5.31–19.30%) and γ-terpinene (3.38–16.42%). The composition <strong>of</strong> essential oil<br />
<strong>of</strong> oregano was affected by soil moisture regimes using fresh and saline water irrigation and potassium<br />
humate fertilization.<br />
Keywords: Origanum vulgare L., essential oil, potassium humate, soil moisture regime, saline<br />
irrigation, carvacrol<br />
_________________________________________________________________________________<br />
INTRODUCTION<br />
The genus Origanum belongs to the family <strong>of</strong> Lamiaceae (Labiatae) and includes many species that are<br />
commonly found as wild plants in the Mediterranean areas (Skoula and Harborne, 2002). Because <strong>of</strong><br />
special compositions <strong>of</strong> essential oil the leaves <strong>of</strong> Origanum plants are widely used as a very popular<br />
spice for food production. Origanum vulgare L. is the widest spread among all the species within the<br />
genus which distributed all over, Europe, West and Central Asia up to Taiwan, North Africa, and<br />
America (Goliaris et al., 2002; Ietswaart, 1980). Traditionally, leaves and flowers <strong>of</strong> oregano are used<br />
in Lithuania mostly for their beneficial properties to cure cough, sore throats, relieve digestive<br />
complaints, and probably stimulate the appetite (Ien et al., 2008). The volatile oil <strong>of</strong> oregano has been<br />
used traditionally for respiratory disorders, indigestion, dental caries, rheumatoid arthritis and urinary<br />
tract disorders (Ertas et al., 2005). The essential oil <strong>of</strong> oregano is composed <strong>of</strong> carvacrol as dominant<br />
component, followed by p-cymene, γ- terpinene, germacrene D, and thymol (Azizi et al., 2009;<br />
Dorman and Deans, 2004; Horne et al., 2001; Said-Al Ahl et al., 2009 a, b; Veldhuizen et al., 2007).<br />
Recently, this spice plant has drawn more attention <strong>of</strong> consumers due to the antimicrobial, antifungal,<br />
insecticidal and antioxidative effects <strong>of</strong> this herb on humanhealthy (Bakkali et al., 2008; Jaloszynski et<br />
al., 2008; Kulisic et al., 2004; Lopez et al., 2007; Soylu et al., 2007).<br />
125
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
The commercial value <strong>of</strong> an aromatic and <strong>of</strong> a medicinal plant could be reflected by the composition <strong>of</strong><br />
their essential oils. The quality <strong>of</strong> oregano is determined mainly by the essential oil content and its<br />
composition. Both parameters may vary considerably depending on genotypes and cultivation<br />
conditions (D’antuono et al., 2000; Novak et al., 2003). In addition, the essential oil content <strong>of</strong> oregano<br />
leaves and its components seem to be strongly influenced by environmental problems, especially<br />
water/salt stress (Charles et al., 1990) and deficiency and inadequate mineral nutrients (Stutte, 2006).<br />
Salinity is one <strong>of</strong> the major factors that affect plant growth; it is a serious problem in many areas <strong>of</strong> the<br />
world causing considerable loss in agricultural production (Bray et al., 2000; Shao et al., 2008; Wu et<br />
al., 2007). Soil salinity resulting from natural processes or from crop irrigation with saline water,<br />
occurs in many arid and semi-arid regions <strong>of</strong> the world (Lauchli and Epstein, 1990). In Egypt, saline<br />
water is used for irrigation in some areas. In the same time, under the arid climatic conditions<br />
prevailing in Egypt and associated with the perennial irrigation practices, imperfect drainage system,<br />
continuous increase <strong>of</strong> water–table level and the relatively high salinity levels <strong>of</strong> water sources<br />
particularly in the new reclaimed land, the salinization <strong>of</strong> Egyptian soils rapidly going to be an acute<br />
problem.<br />
Similar to other Lamiaceae species, however, uniformity in essential oil content and composition and<br />
consistency in growth and development are especially susceptibility to environmental stress due to<br />
plant heterogeneity. Thus, crop yields and quality in major oregano production regions that are<br />
frequently subject to dry periods can fluctuate (Al-Amier and Craker, 2007). The use <strong>of</strong> irrigation over<br />
the past several years to promote crop growth has increased the salt content <strong>of</strong> the soil, frequently<br />
forcing growers to apply 10% to 20% excess water to lower salt concentrations in the root zone (Arndt<br />
et al., 2001; Mohamed et al., 2002; Takabayashi and Dick 1996; Takabayashi et al., 1994). Water<br />
stress in plants from a lack <strong>of</strong> moisture or from drought induced by salt stress is associated with many<br />
metabolic changes, including essential oil metabolites. In addition, the water supply is one <strong>of</strong> the most<br />
determinative cultivation conditions which significantly affect the yield and essential oil content <strong>of</strong><br />
various spices and herb crops (Aziz et al., 2008; Mohamed et al., 2002; Singh and Ramesh, 2000;<br />
Singh et al., 2000, 2002; Zehtab- Salmasi et al., 2001). In most cases Origanum plants must be<br />
irrigated during the cultivation period to obtain a good yield. For example during cultivation <strong>of</strong><br />
Origanum dictamnus in Crete (Greece), irrigation was necessary for two harvests in 1 year (Skoula and<br />
Kamenopoulos, 1997). Practically, the time at which the plants are irrigated is important for the<br />
efficiency <strong>of</strong> irrigation. For example, appropriate irrigation strategies showed a great potential for<br />
improvement <strong>of</strong> the yield <strong>of</strong> monoterpenes in field-grown spearmint and rosemary (Delfine et al.,<br />
2005). Dunford and Vazquez (2005) reported that herb yield <strong>of</strong> Mexican oregano (Lippia Berlandieri<br />
Schauer) increased significantly with increasing moisture and the amount <strong>of</strong> water received by the plant<br />
did not have a significant effect on the thymol and carvacrol content <strong>of</strong> the oil.<br />
The improvement <strong>of</strong> plant nutrition can contribute to increased resistance and production when the crop<br />
is submitted to water stress. However, the content <strong>of</strong> essential oils and their composition are affected by<br />
fertilization.<br />
Humic acid (HA) is one <strong>of</strong> the major components <strong>of</strong> humus. Humates have long been used as a soil<br />
conditioner, fertilizer and soil supplement (Albayrak and camas, 2005). Humic acid can be used as<br />
growth regulate-hormone level improve plant growth and enhance stress tolerance (Albayrak and<br />
Camas, 2005; Piccola et al., 1992; Tan and Nopamornbodi, 1979). Fortun et al., 1989 and Kononova,<br />
1966 reported that humic acid improve soil structure and change physical properties <strong>of</strong> soil, promote<br />
the chelation <strong>of</strong> many elements and make these available to plants, aid in correcting plant chlorisis,<br />
enhancement <strong>of</strong> photosynthesis density and plant root respiration has resulted in greater plant growth<br />
with humate application (Chen and Avid, 1990; Smidova, 1960). Increase the permeability <strong>of</strong> plant<br />
membranes due to humate application resulted in improve growth <strong>of</strong> various groups <strong>of</strong> beneficial<br />
microorganisms, accelerate cell division, increased root growth and all plant organs for a number <strong>of</strong><br />
horticultural crops and turfgrasses, as well as, the growth <strong>of</strong> some trees, Russo and Berlyn (1990),<br />
Sanders et al. (1990) and Pioncelot (1993).<br />
So far, there is no report on the yield and composition <strong>of</strong> the essential oil <strong>of</strong> Origanum vulgare L.<br />
plants cultivated under this experimental condition in literature.<br />
The aim <strong>of</strong> the present research was to investigate to evaluate oregano plants grown under osmotic<br />
stress conditions and using organic fertilizer treatments to raise the tolerant <strong>of</strong> this plant to stress<br />
conditions, and also to provide information on the composition <strong>of</strong> Origanum vulgare volatile oil and<br />
its variability among osmotic stress conditions.<br />
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MATERIALS AND METHODS<br />
A pot trail study was carried out during the two successive seasons <strong>of</strong> 2007/2008 and 2008/2009 under<br />
the natural conditions <strong>of</strong> the greenhouse <strong>of</strong> the National Research Center, Dokki, Giza, Egypt. The<br />
physical and chemical analyses <strong>of</strong> the soil were determined according to Jackson, 1973. The soil<br />
texture was sandy loam, having a physical composition as follows: 45.70% sand, 28.40% silt, 25.90%<br />
clay and 0.85% organic matter. The results <strong>of</strong> soil chemical analysis were as follows: pH= 8.05; E.C<br />
(dsm -1 ) = 0.81; and total nitrogen =0.09 %; available phosphorus =2.26mg/100gram; potassium= 18.85<br />
mg/100gram; field capacity (F.C.) and wilting point (W.P.) were determined according to the pressure<br />
membrane methods described by Black, 1965. Field capacity, permanent wilting point, available soil<br />
moisture (A.S.M) and bulk density (B.D.), as means over the two seasons were 34.0 %, 16.0 % 18.0 %<br />
and 1.36 g/cm 3 , respectively.<br />
Seeds <strong>of</strong> oregano were obtained from Jellitto Standensamen Gmbh, Schwarmstedt, Germany. The<br />
seeds were sown in the nursery on 15 th November during both seasons. The seedlings were transplanted<br />
into pots (30 cm diameter, 50 cm depth) on the 15 th February <strong>of</strong> each season. Each pot contained three<br />
seedlings and was placed in full sun light. Each pot was filled with 10 kg <strong>of</strong> air dried soil. The soil<br />
related to the typic torrifluvents (based on USDA, 1996). Two levels <strong>of</strong> potassium humate (0.0 and 1.5<br />
g pot -1 ) was applied to the soil with water irrigation application at three equal portions before each cut<br />
in both seasons. Potassium humate which was used in this study is produced by Leili Agrochemistry<br />
Co., LTD, China and its properties are shown in Table (1). Then after one month from transplanting,<br />
irrigation treatments were applied to the oregano plants (90, 60 and 30% available soil moisture) equal<br />
to 32.20., 26.80 and 21.40 soil moisture. The pots were separated into two sets, the first set irrigated<br />
with tap water (0.40 dsm -1 ), and the second set irrigated with Nacl solution (4 dsm -1 ). Pots were<br />
weighted daily and when soil moisture percentage reached the aforementioned points, pots were<br />
irrigated to reach field capacity (34.0% soil moisture). The differences between the needed soil<br />
moisture for the previous treatments and field capacity were calculated and added to the pots in the<br />
different treatments. The experimental layout was factorial experiment in complete randomized design<br />
(CRD) with three replications. Each replicate contained ten pots, while the pot contained three plants.<br />
Herbal fresh weight (g plant -1 ) <strong>of</strong> each replicate was determined in the first, second and third cuts at<br />
31 May, 31 July and 30 September, respectively before flowering stage in both seasons. Essential oil<br />
content was determined by hydro-distillation for 3 hours by submitting fresh herb (100 g) for each<br />
replicate at each cut in both seasons in modified Clevenger apparatus (Guenther, 1961). Essential oil<br />
percentage <strong>of</strong> each replicate was determined and expressed as (%), while essential oil yield per plant<br />
was expressed as ml plant -1 . The essential oils <strong>of</strong> each treatment were collected and dehydrated over<br />
anhydrous sodium sulphate and kept in a refrigerator until gas-liquid chromatography (GLC) analyses.<br />
The GLC analysis <strong>of</strong> the essential oil samples was carried out in the second season using a Hewlett<br />
Packard gas chromatograph apparatus at the Central Laboratory <strong>of</strong> the National Research Center<br />
(NRC) with the following specifications: instruments: Hewlett Packard 6890 series, column; HP<br />
(Carbwax 20M, 25m length x 0.32mm I.D), film thickness: 0.3mm, sample size: 1µl, oven temperature:<br />
60-190°C, Program temperature: 60°C/2min, 8°C/min, 190°C/25min, injection port<br />
temperature:240°C, carrier gas: nitrogen, detector temperature (FID): 280°C, flow rate: N2 3ml/min.,<br />
H2 3ml/min., air 300ml/min. Main compounds <strong>of</strong> the essential oil were identified by matching their<br />
retention times with those <strong>of</strong> the authentic samples that were injected under the same conditions. The<br />
relative percentage <strong>of</strong> each compound was calculated from the peak area corresponding to each<br />
compound. Except for the constituents <strong>of</strong> the essential oils, the data <strong>of</strong> this experiment were statistically<br />
analyzed according to Snedcor and Cochran (1981).<br />
A.Herb fresh yield<br />
RESULTS AND DISCUSSIONS<br />
Effect <strong>of</strong> water stress using fresh or saline water irrigation<br />
Data in Table (2) clear the effect <strong>of</strong> water stress and potassium humate on the productivity <strong>of</strong> oregano<br />
plant using saline and fresh water irrigation. Under water stress, increase in available soil moisture<br />
significantly enhanced the fresh herb yield in all cuts <strong>of</strong> both seasons. Increasing water amounts<br />
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increased herb fresh weight. The highest mean values due to irrigation treatments were recorded with<br />
plants that received the highest amounts <strong>of</strong> water. The pronounced effect <strong>of</strong> increased irrigation on<br />
fresh herb yield may be attributed to the availability <strong>of</strong> sufficient moisture around the root concentrated<br />
and thus a greater proliferation <strong>of</strong> root biomass resulting in the higher absorption <strong>of</strong> nutrients and water<br />
leading to production <strong>of</strong> higher vegetative biomass (Singh et al., 1997). On the other hand, increasing<br />
levels <strong>of</strong> water stress reduce growth and yield due to reduction in photosynthesis and plant biomass.<br />
Under increasing water- stress levels photosynthesis was limited by low Co2 availability due to<br />
reduced stomatal and mesophyll conductance. Drought stress is associated with stomatal closure and<br />
thereby with decreased Co2 fixation. The superiority <strong>of</strong> the plants that received the highest rate <strong>of</strong><br />
irrigation treatments in producing the heaviest total plant fresh weight was in agreement with that <strong>of</strong> El-<br />
Naggar et al. (2004); Moeini Alishah et al. (2006); Said-Al Ahl and Abdou (2009); Said-Al Ahl et al.<br />
(2009 a, c) .<br />
Data tabulated in Table (2) show that fresh weight <strong>of</strong> herb (g plant -1 ) decreased significantly with<br />
increment <strong>of</strong> saline irrigation conditions in all cuts during both seasons. The inhibitory effect <strong>of</strong><br />
salinity was also found by (Abd El-Hady, 2007; Abd El-Wahab, 2006; Baghalian et al., 2008; Belaqziz<br />
et al., 2009; Ozturk et al., 2004; Razmjool et al., 2008; Shalan et al., 2006; Turhan and Eris, 2007).<br />
Saline conditions reduce the ability <strong>of</strong> plants to absorb water causing rapid reductions in growth rate,<br />
and induce many metabolic changes (Epstein, 1980). Also, salt stress with osmotic, nutritional and<br />
toxic effects prevents growth in many plant species (Cheeseman, 1988; Hasegawa et al., 1986).<br />
Therefore, the reduction in growth was explained by lower osmotic potential in the soil, which leads to<br />
decreased water uptake, reduced transpiration, and closure <strong>of</strong> stomata, which is associated with the<br />
reduced growth (Ben-Asher et al., 2006; Levitt, 1980). In general, the mechanisms <strong>of</strong> salinity effect on<br />
plant growth were reported by Meiri and Shalhavet (1973) who attributed the effect <strong>of</strong> salinity to the<br />
following points: (a) the distribution <strong>of</strong> salts within the plant cells may result in turgor reduction and<br />
growth retardations. Also, salinity affects root and stomatal resistance to water flow, (b) the balance<br />
between root and shoot hormones changes considerably under saline conditions, (c) salinity changes<br />
the structure <strong>of</strong> the chloroplasts and mitochondria and such changes may interfere with normal<br />
metabolism and growth, (d) salinity increases respiration and reduces photosynthesis products available<br />
for growth.<br />
Effect <strong>of</strong> potassium humate application<br />
Also, data reported in Table (2) showed that foliar application <strong>of</strong> humic acid caused significantly<br />
positive trend in increasing herb fresh yield (g plant -1 ). Similar results were reported by Said-Al Ahl et<br />
al. (2009, b) on Origanum vulgare and Zaghloul et al. (2009) on Thuja orientalis who indicated that<br />
spraying the plants with potassium humate increased growth compared with control plants due to the<br />
direct effect <strong>of</strong> humic acid on solubilization and transport <strong>of</strong> nutrients. These results are in accordance<br />
with those obtained by Norman et al. (2004) on marigolds and peppers and number <strong>of</strong> fruits <strong>of</strong><br />
strawberries. Chen and Avaid (1990) added that humic substances have a very pronounced influence on<br />
the growth <strong>of</strong> plant roots thought enhance root initiation which known as root stimulator. Humic acid<br />
improve growth <strong>of</strong> plant foliage and roots where, Vaughan (1974) proposed that humic acids may<br />
primarily increase root growth by increasing cell elongation or root cell membrane permeability,<br />
therefore increased water uptake by increased plant roots, as well as it can produce root systems by<br />
increasing branching and number <strong>of</strong> fine roots, as a result potentially increase nutrients uptake by<br />
increase root surface area (Rauthan and Schnitzer, 1981).<br />
Effect <strong>of</strong> interaction<br />
There was a significant difference in most <strong>of</strong> interaction treatments between water or salt stress and<br />
potassium humate application. Increment the available soil moisture using saline or fresh water<br />
combined with potassium humate enhanced the fresh herb yield. The irrigation applied at 90%<br />
available soil moisture using fresh water irrigation, combined with potassium humate gave the best<br />
result <strong>of</strong> fresh herb yield in the all cuts during both seasons.<br />
B. Essential oil production<br />
Effect <strong>of</strong> water stress using fresh or saline water irrigation<br />
In all cuts in both seasons, both water quantities using saline and fresh water irrigation and potassium<br />
humate application and their interaction affected the content <strong>of</strong> essential oils in oregano (Tables 3, 4).<br />
The mean values <strong>of</strong> essential oils due to water irrigation treatments showed that increasing water<br />
supply from 30% to 60% available soil moisture increased essential oil percentage. Increasing water<br />
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supply from 60% to 90% available soil moisture decreased percentage <strong>of</strong> essential oils. In other words,<br />
the medium stress condition (60% available soil moisture treatment) accelerated the production <strong>of</strong><br />
essential oils, while the severe stress conditions due to water (40% available soil moisture treatment)<br />
decreased the biosynthesis <strong>of</strong> the essential oils. On the contrary, essential oil yield increased with<br />
increment <strong>of</strong> available soil moisture (Table 4).<br />
Table (3) explains that salt condition significant decreased essential oil % at all cuts in both seasons.<br />
With similar, essential oil yield also was significant decreased at all cuts <strong>of</strong> both seasons as a result <strong>of</strong><br />
salt stress (Table 4). The inhibitory effect <strong>of</strong> high level <strong>of</strong> salinity was also found by many investigators<br />
(Abd El-Wahab, 2006; Baghalian et al., 2008; Ozturk et al., 2004; Razmjoo et al., 2008; Shalan et al.,<br />
2006). The reduction <strong>of</strong> essential oil yield by salinity may be due to a decrease in growth characters<br />
and/or essential oil %. Salt stress may also affect the essential oil accumulation indirectly through its<br />
effects on either net assimilation or the partitioning <strong>of</strong> assimilate among growth and differentiation<br />
processes (Charles et al., 1990).<br />
Penka (1978) showed that the formation and accumulation <strong>of</strong> essential oil in plants was explained as<br />
due to the action <strong>of</strong> environmental factors. It might be claimed that the formation and accumulation <strong>of</strong><br />
essential oil was directly dependent on perfect growth and development <strong>of</strong> the plants producing oils.<br />
The decrease in oil production might be due to the decrease in plant anabolism.<br />
Effect <strong>of</strong> potassium humate application<br />
Essential oil percent and yield (ml plant -1 ) in oregano herb were significantly increased as a result <strong>of</strong><br />
foliar application with K-humate (Tables 3, 4). Said-Al Ahl et al. (2009, b) and Zaghloul et al. (2009)<br />
reported that humate application lead to increase oil content in Origanum vulgare and Thuja orientalis,<br />
respectively. From the above mentioned results, it could be concluded that foliar application <strong>of</strong> Khumate<br />
promoted growth and possessed the best oil percentage and yield (ml plant -1 ) in oregano plant.<br />
Effect <strong>of</strong> interaction<br />
Generally, the maximum essential oil content was observed in the fresh herb <strong>of</strong> plants that irrigated<br />
using fresh water at 60% ASM and sprayed with 1% K-humate in the all cuts during both seasons. In<br />
addition, spraying oregano plants with K-humate caused an increase in the essential oil yield (Table 4).<br />
Generally, the highest essential oil yield (ml plant -1 ) was obtained from plants irrigated using fresh<br />
water at 90% ASM and sprayed at 1% K-humate in all cuts <strong>of</strong> both seasons. The increment <strong>of</strong> essential<br />
oil yield may be obtained as a result <strong>of</strong> increment herb weight and/or essential oil %.<br />
Essential oil composition <strong>of</strong> oregano<br />
Totally, 20 constituents were identified for the oregano essential oil (Tables 5, 6). Carvacrol content<br />
was the dominant constituent <strong>of</strong> the essential oil for all samples tested, ranging from 46.44% to<br />
77.96%. The second major constituent was p-cymene (ranging from 5.31% to 19.30%) and the third<br />
one was γ-terpinene (ranging from 3.38% to 16.42%). The other main constituents were α-pinene (0-<br />
5.39%), α-terpinene (0-5.39%), α-thujene (0-5.05%), germacrene D (0-2.91%), thymol (0-2.76%),<br />
caryophyllene (0-2.70%), terpineol-4-ol (0-1.56%) and β-pinene (0-1.19%). Other constituents such as<br />
linalool, limonene, borneol, α-terpineol, bornyl acetate, carvacrol acetate, elemene, cadinene and<br />
caryophyllene oxide were present in amount less the 1%.<br />
In second cut <strong>of</strong> second season, among water and saline stress, the carvacrol percentage <strong>of</strong> essential oil<br />
was increased by raising amount <strong>of</strong> fresh water irrigation and irrigation at 90% ASM gave a higher<br />
value (77.96%), 60% ASM (67.17%) and 30% ASM gave a lower value (60.36%), but there was<br />
decrease in this regard by raising amount <strong>of</strong> saline water irrigation and irrigation at 30% ASM gave a<br />
higher content (58.02%), 90% ASM (57.79%) and 60% ASM gave a lower content (46.44%). Whereas,<br />
p-cymene was decreased by raising amount <strong>of</strong> fresh and saline water irrigation and a higher content <strong>of</strong><br />
this component was resulted from irrigation at 30% ASM (15.63 and 16.94% using fresh and saline<br />
water, respectively), 60% ASM fresh water and 90% ASM saline water (11.64 and 16.03%,<br />
respectively) and a lower content (8.76 and 13.29%, resulted from 90% ASM fresh water and 60%<br />
ASM saline water, respectively). Correspondingly, the percentage <strong>of</strong> γ-terpinene was decreased by<br />
raising amount <strong>of</strong> fresh water irrigation and irrigation at 30% ASM gave a higher value (7.65%), 60%<br />
ASM (6.61%) and 90% ASM gave a lower value (3.56%), but there was increase in this regard by<br />
raising amount <strong>of</strong> saline water irrigation and irrigation at 90% ASM gave a higher content (12.94%),<br />
30% ASM (11.63%) and 60% ASM gave a lower content (11.32%), Table (5). It is clear that saline<br />
water irrigation increased the biosynthesis <strong>of</strong> p-cymene and γ-terpinene, while the apposite was true<br />
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with carvacrol. It is well known p-cymene transforms to thymol or carvacrol and the environmental<br />
conditions affect the rate <strong>of</strong> transformation (Aziz et al., 2008; Omer, 1999).<br />
From Table (6) it can be observed the differences between three major constituents <strong>of</strong> essential oil <strong>of</strong><br />
oregano supplying with a water level <strong>of</strong> 90% available soil moisture and without / with 1.5 g K-humate<br />
pot -1 in three cuttings, carvacrol was higher for plants irrigated with a fresh water alone in second cut<br />
and compared to other treatments but, the plants irrigated with a saline water alone in first cut<br />
contained a lower content. On the contrary p-cymene and γ-terpinene were the highest by using saline<br />
water irrigation and with K-humate in first cut and the lowest content from the plants irrigated with<br />
fresh water alone in third cut. Irrigation with 90% ASM with fresh water without potassium humate in<br />
second cut gave the maximum value <strong>of</strong> carvacrol content (77.96%), while irrigation with 90% ASM<br />
with fresh water without potassium humate in first cut gave the highest values for both p-cymene<br />
(10.99%) and γ-terpinene (8.41%). Under saline water irrigation the maximum values for both pcymene<br />
(19.30%) and γ-terpinene (16.42%) were obtained as a result <strong>of</strong> 90% ASM with potassium<br />
humate in first cut, while 90% ASM with potassium humate in second cut gave the highest value <strong>of</strong><br />
carvacrol (63.17%).<br />
Table (7) indicates that saline water irrigation decreased the mean value <strong>of</strong> carvacrol and on the<br />
contrary there was increased in p-cymene and γ-terpinene mean values by using saline water irrigation.<br />
Whereas, mean values <strong>of</strong> carvacrol, p-cymene and γ-terpinene were increased by application <strong>of</strong> Khumate.<br />
Also, mean values <strong>of</strong> carvacrol, p-cymene and γ-terpinene were affected by cuttings. For<br />
carvacrol, third cut recorded the highest mean value followed by second cut and then first cut.γterpinene<br />
has adverse behavior, first cut resulted the highest mean value followed by second cut and<br />
then third cut. However, the highest mean value <strong>of</strong> p-cymene resulted from second cut and third cut<br />
recorded the lowest mean value.<br />
Second cut was effective in raising the productivity <strong>of</strong> the essential oil yield. Table (8) show that saline<br />
water irrigation decreased the mean value <strong>of</strong> carvacrol and on the contrary there was increased in pcymene<br />
and γ-terpinene mean values by using saline water irrigation. Among soil moisure levels, the<br />
carvacrol mean value <strong>of</strong> essential oil was the highest at 90% ASM and 60% ASM obtained the lowest<br />
mean value. Also, the mean values <strong>of</strong> p-cymene and γ-terpinene were the highest for 30% ASM<br />
followed by 60% ASM and then 90% ASM.<br />
CONCLUSIONS<br />
Our study showed that herbal production and essential oil content <strong>of</strong> Origanum vulgare L. can be<br />
significantly affected by environmental and agronomical conditions including potassium humate<br />
fertilization and soil moisture regime using fresh and saline water irrigation. Application <strong>of</strong> potassium<br />
humate increase herb fresh yield and essential oil content <strong>of</strong> oregano herbage. Herbal fresh yield and<br />
essential oil % and oil yield ml plant -1 were significant decreased by using a saline water irrigation<br />
compared to fresh water. Supplying plants with a water level <strong>of</strong> 90% available soil moisture was<br />
effective in raising the productivity <strong>of</strong> herb and yield <strong>of</strong> essential oil, but 60% available soil moisture<br />
was effective in essential oil percentage, whereas 30% available soil moisture significantly decreased<br />
herbal fresh yield and essential oil % and oil yield ml plant -1 .The interaction between 90% available<br />
soil moisture <strong>of</strong> fresh water and with 1.5 g pot -1 k-hum ate gave the best results for herb and yield <strong>of</strong><br />
essential oil. Essential oil % recorded their maximum value from plants irrigated with 60% ASM <strong>of</strong><br />
fresh water combined with 1.5 g pot -1 K-humate. Whereas percentage <strong>of</strong> main compounds <strong>of</strong> essential<br />
oil such as carvacrol, γ-terpinene and p-cymene affected by these treatments. Supplying plants with a<br />
water level <strong>of</strong> 90% available soil moisture <strong>of</strong> fresh water alone in second cut contained the highest<br />
value <strong>of</strong> carvacrol, but p-cymene and γ-terpinene recorded their maximum values by irrigating<br />
Origanum vulgare with a saline water level <strong>of</strong> 90% available soil moisture and with k-humate in first<br />
cut.<br />
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TABLES<br />
Table 1. Guaranteed analysis and physical data <strong>of</strong> Humic total<br />
Guaranteed analysis<br />
Humic acid 80%<br />
Potassium (K2O) 10-12%<br />
Zn, Fe, Mn, etc., 100ppm<br />
Physical Data<br />
Appearance Black powder<br />
pH 9-10<br />
Water solubility < 98%<br />
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Table 2. Effect <strong>of</strong> water stress using saline and fresh water irrigation, K-humate fertilizer and their interaction treatments on the herb fresh weight <strong>of</strong> oregano<br />
plants during the two seasons.<br />
K-humate<br />
132<br />
First Season<br />
Water<br />
Herb fresh weight (g plant<br />
and salt<br />
stress<br />
-1 )<br />
Without<br />
K-humate<br />
First cut<br />
K-humate Mean<br />
Without<br />
K-humate.<br />
Second cut<br />
K-humate. Mean<br />
Without<br />
K-humate<br />
Third cut<br />
K-humate Mean<br />
S1 2.41 4.58 3.49 3.72 6.45 5.08 1.05 1.58 1.31<br />
S2 4.18 7.77 5.97 7.50 10.07 8.78 3.13 5.02 4.08<br />
S3 5.71 10.53 8.12 8.96 17.43 13.20 4.38 7.30 5.84<br />
S4 1.58 2.02 1.80 2.03 2.48 2.25 0.61 0.75 0.68<br />
S5 2.02 2.49 2-25 2.76 3.01 2.88 0.94 1.24 1.09<br />
S6 2.72 3.21 2-96 3.59 4.42 4.00 1.83 2.02 1.92<br />
Mean 3.10 5.10 4.76 7.31 6.03 1.99 2.98<br />
L.S.D. at 5% K-humate =0.056<br />
K-humate = 0.046<br />
K-humate = 0.034<br />
Stress = 0.098<br />
Stress = 0.079<br />
Stress = 0.059<br />
Interaction =0.138<br />
Interaction = 0.113<br />
Interaction =0.083<br />
S1 2.47 4.58 3.53 3.69<br />
Second Season<br />
6.45 5.07 1.03 5.03 3.03<br />
S2 4.19 7.69 5.94 7.53 10.17 8.85 3.10 7.20 5.15<br />
S3 5.70 10.75 8.23 8.88 17.28 13.08 4.44 0.58 2.51<br />
S4 1.49 2.02 1.75 1.97 2.43 2.20 0.58 0.71 0.64<br />
S5 2.05 2.42 2.23 2.72 3.05 2.88 0.94 1.10 1.02<br />
S6 2.61 3.15 2.88 3.65 4.39 4.02 1.88 2.07 1.97<br />
Mean 3.08 5.10 4.74 7.29 1.99 2.78<br />
L.S.D. at 5% K-humate =0.050<br />
K-humate = 0.042<br />
K-humate = 0.039<br />
Stress = 0.087<br />
Stress = 0.073<br />
Stress = 0.067<br />
Interaction =0.123<br />
Interaction =0.103<br />
Interaction =0.055<br />
S-stress; S1, S2, S3= irrigation <strong>of</strong>: 30, 60, 90% available soil moisture using fresh water; S4, S5, S6= irrigation <strong>of</strong>: 30, 60, 90% available soil moisture using<br />
saline water
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 3. Effect <strong>of</strong> water stress using saline and fresh water irrigation, K-humate fertilizer and their interaction treatments on the herb fresh volatile oil (%) <strong>of</strong><br />
oregano plants during the two seasons.<br />
K-humate<br />
133<br />
First Season<br />
Water<br />
Volatile oil (%)<br />
and salt<br />
stress<br />
Without<br />
K-humate<br />
First cut<br />
K-humate Mean<br />
Without<br />
K-humate.<br />
Second cut<br />
K-humate. Mean<br />
Without<br />
K-humate<br />
Third cut<br />
K-humate Mean<br />
S1 0.533 0.633 0.583 0.450 0.533 0.491 0.416 0.433 0.425<br />
S2 0.650 0.750 0.700 0.533 0.633 0.583 0.500 0.583 0.541<br />
S3 0.600 0.683 0.641 0.500 0.600 0.550 0.466 0.533 0.500<br />
S4 0.366 0.383 0.375 0.316 0.366 0.341 0.233 0.266 0.250<br />
S5 0.450 0.483 0.466 0.433 0.483 0.458 0.383 0.400 0.391<br />
S6 0.433 0.466 0.450 0.433 0.466 0.450 0.350 0.383 0.366<br />
Mean 0.505 0.566 0.444 0.513 0.391 0.433<br />
L.S.D. at 5% K-humate = 0.0157<br />
K-humate = 0.0143<br />
K-humate = 0.0184<br />
Stress = 0.0275<br />
Stress = 0.0247<br />
Stress = 0.0319<br />
Interaction =N.S<br />
Interaction = 0.0349<br />
Interaction =0.0451<br />
S1 0.516 0.633 0.575 0.433<br />
Second Season<br />
0.533 0.483 0.400 0.433 0.416<br />
S2 0.633 0.766 0.700 0.533 0.616 0.575 0.500 0.583 0.541<br />
S3 0.616 0.666 0.641 0.500 0.583 0.541 0.450 0.533 0.491<br />
S4 0..383 0.416 0.400 0.300 0.383 0.341 0.250 0.316 0.283<br />
S5 0.483 0.500 0.491 0.466 0.466 0.466 0.366 0.383 0.375<br />
S6 0.433 0.450 0.441 0.416 0.433 0.425 0.366 0.383 0.375<br />
Mean 0.511 0.572 0.541 0.441 0.502 0.388 0.438<br />
L.S.D. at 5% K-humate = 0.0150<br />
K-humate = 0.0190<br />
K-humate = 0.0178<br />
Stress = 0.0260<br />
Stress = 0.0329<br />
Stress = 0.0308<br />
Interaction =0.0368<br />
Interaction =0.0466<br />
Interaction =0.0436<br />
S-stress; S1, S2, S3= irrigation <strong>of</strong>: 30, 60, 90% available soil moisture using fresh water; S4, S5, S6= irrigation <strong>of</strong>: 30, 60, 90% available soil moisture using<br />
saline water
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 4. Effect <strong>of</strong> water stress using saline and fresh water irrigation, K-humate fertilizer and their interaction treatments on the volatile oil yield (ml plant -1 )<br />
<strong>of</strong> oregano plants during the two seasons.<br />
K-humate<br />
134<br />
First Season<br />
Water<br />
Oil yield (ml plant<br />
and salt<br />
stress<br />
-1 )<br />
Without<br />
K-humate<br />
First cut<br />
K-humate Mean<br />
Without<br />
K-humate.<br />
Second cut<br />
K-humate. Mean<br />
Without<br />
K-humate<br />
Third cut<br />
K-humate Mean<br />
S1 0.0128 0.0289 0.0209 0.0167 0.0353 0.0260 0.0044 0.0068 0.0056<br />
S2 0.0271 0.0582 0.0427 0.0400 0.0528 0.0464 0.0153 0.0293 0.0223<br />
S3 0.0342 0.0725 0.0534 0.0448 0.0916 0.0682 0.0204 0.0389 0.0296<br />
S4 0.0058 0.0077 0.0068 0.0064 0.0091 0.0078 0.0014 0.0016 0.0015<br />
S5 0.0091 0.0121 0.0106 0.0120 0.0146 0.0133 0.0036 0.0050 0.0043<br />
S6 0.0118 0.0150 0.0134 0.0156 0.0206 0.0181 0.0064 0.0078 0.0071<br />
Mean 0.0168 0.0324 0.0226 0.0373 0.0086 0.0149<br />
L.S.D. at 5% K-humate = 0.00076<br />
K-humate = 0.0048<br />
K-humate = 0.0005<br />
Stress = 0.00281<br />
Stress = 0.0083<br />
Stress = 0.0009<br />
Interaction =0.00188<br />
Interaction = 0.0118<br />
Second Season<br />
Interaction =0.0013<br />
S1 0.0154 0.0290 0.0222 0.0160 0.0344 0.0252 0.0041 0.0065 0.0053<br />
S2 0.0265 0.0589 0.0427 0.0387 0.0627 0.0507 0.0155 0.0294 0.0224<br />
S3 0.0351 0.0717 0.0534 0.0444 0.1008 0.0726 0.0799 0.0384 0.0591<br />
S4 0.0057 0.0337 0.0197 0.0059 0.0093 0.0076 0.0014 0.0023 0.0018<br />
S5 0.0099 0.0121 0.0110 0.0127 0.0142 0.0134 0.0036 0.0046 0.0041<br />
S6 0.0113 0.0142 0.0128 0.0152 0.0190 0.0171 0.0069 0.0079 0.0074<br />
Mean 0.0173 0.0366 0.0270 0.0221 0.0401 0.0186 0.0148<br />
L.S.D. at 5% K-humate = 0.0073<br />
K-humate = 0.0012<br />
K-humate = 0.0171<br />
Stress = 0.0126<br />
Stress = 0.0021<br />
Stress = 0.0297<br />
Interaction =0.0178<br />
Interaction =0.0030<br />
Interaction =0.0420<br />
S-stress; S1, S2, S3= irrigation <strong>of</strong>: 30, 60, 90% available soil moisture using fresh water; S4, S5, S6= irrigation <strong>of</strong>: 30, 60, 90% available soil moisture using<br />
saline water
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 5. Essential oil composition (%) <strong>of</strong> Origanum vulgare L. plants grown under different levels <strong>of</strong><br />
Available soil moisture using fresh and saline water irrigation at second cut in 2009 season.<br />
Compounds<br />
135<br />
Treatments<br />
Irrigation with fresh water Irrigation with saline water<br />
30% ASM 60% ASM 90% ASM 30% ASM 60% ASM 90% ASM<br />
���thujene -- -- 0.33<br />
���pinene -- 0.11 0.08<br />
���pinene 0.56 0.61 0.11<br />
��terpinene<br />
0.45 0.28 0.38<br />
P-cymene<br />
15.63 11.64 8.76<br />
limonene<br />
γ- terpinene<br />
linalool<br />
borneol<br />
Terpinene-4-ol<br />
��terpineol<br />
thymol<br />
Bornyl acetate<br />
carvacrol<br />
Carvacrol acetate<br />
elemene<br />
0.70 0.46 0.30<br />
7.65 6.61 3.56<br />
0.64 0.35 0.54<br />
0.90 0.76 0.03<br />
0.85 0.51 0.40<br />
0.19 0.20 0.27<br />
1.87 1.55 0.98<br />
0.16 0.19 0.06<br />
60.36 67.17 77.96<br />
0.59 0.41 0.59<br />
0.29 0.21 0.36<br />
�caryophyllene 0.14 0.45 0.40<br />
germacrene D<br />
cadinene<br />
caryephyllene oxide<br />
Identified compounds<br />
0.59 1.61 0.83<br />
0.05 0.09 0.01<br />
-- -- 0.01<br />
91.62 93.21 95.96<br />
Irrigation <strong>of</strong>: 30, 60, 90% ASM– <strong>of</strong> available soil moisture<br />
-- 5.05<br />
-- 2.70<br />
-- 0.75<br />
1.62 5.39<br />
16.94 13.29<br />
-- 0.49<br />
11.63 11.32<br />
-- 0.41<br />
-- 1.89<br />
-- 1.56<br />
-- --<br />
-- 2.76<br />
-- --<br />
58.02 46.44<br />
-- --<br />
-- 0.45<br />
1.27 2.57<br />
1.52 1.66<br />
-- --<br />
-- 0.87<br />
91.00 97.59<br />
1.15<br />
0.11<br />
0.25<br />
1.53<br />
16.03<br />
--<br />
12.94<br />
0.18<br />
--<br />
0.37<br />
--<br />
0.96<br />
0.24<br />
57.79<br />
0.30<br />
--<br />
1.02<br />
1.07<br />
0.05<br />
0.16<br />
94.05
Compounds<br />
���thujene<br />
���pinene<br />
���pinene<br />
��terpinene<br />
P-cymene<br />
limonene<br />
γ- terpinene<br />
linalool<br />
borneol<br />
Terpinene-4ol<br />
��terpineol<br />
thymol<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 6. Essential oil composition (%) <strong>of</strong> Origanum vulgare L. plants grown with 90% Available soil<br />
moisture using fresh and saline water irrigation and/or k-humate application during three cuts in 2009<br />
season.<br />
Bornyl acetate<br />
carvacrol<br />
Carvacrol<br />
acetate<br />
elemene<br />
�caryophyllene<br />
germacrene D<br />
cadinene<br />
caryephyllene<br />
oxide<br />
Identified<br />
compounds<br />
Treatments<br />
Irrigation with fresh water<br />
Irrigation with saline water<br />
Without K-humate With K-humate<br />
Without K-humate With K-humate<br />
Cut 1 Cut 2 Cut 3 Cut 1 Cut 2 Cut 3 Cut 1 Cut 2 Cut 3 Cut 1 Cut 2 Cut 3<br />
0.21 0.33 0.33 0.31 0.31 1.32 1.50 1.15 1.45 0.77 0.37 1.07<br />
0.23<br />
0.81<br />
0.46<br />
10.99<br />
0.90<br />
8.41<br />
0.40<br />
0.45<br />
0.41<br />
0.20<br />
1.51<br />
0.21<br />
66.04<br />
0.21<br />
0.14<br />
0.36<br />
0.66<br />
0.07<br />
--<br />
92.67<br />
0.08<br />
0.11<br />
0.38<br />
8.76<br />
0.30<br />
3.56<br />
0.54<br />
0.03<br />
0.40<br />
0.27<br />
0.98<br />
0.06<br />
77.96<br />
0.59<br />
0.36<br />
0.40<br />
0.83<br />
0.01<br />
0.01<br />
95.96<br />
0.18<br />
1.04<br />
0.58<br />
5.31<br />
0.53<br />
3.38<br />
0.24<br />
0.23<br />
0.52<br />
--<br />
0.91<br />
0.18<br />
77.04<br />
0.28<br />
0.23<br />
0.22<br />
2.45<br />
0.31<br />
0.19<br />
94.15<br />
0.39<br />
0.65<br />
0.49<br />
9.21<br />
0.36<br />
7.33<br />
0.31<br />
0.40<br />
0.61<br />
0.27<br />
1.27<br />
0.45<br />
67.51<br />
0.81<br />
0.45<br />
0.70<br />
0.48<br />
--<br />
--<br />
91.90<br />
0.31<br />
--<br />
--<br />
10.73<br />
--<br />
5.33<br />
0.36<br />
--<br />
0.43<br />
0.63<br />
1.01<br />
0.30<br />
74.54<br />
0.89<br />
0.45<br />
0.35<br />
0.47<br />
0.02<br />
--<br />
96.13<br />
136<br />
1.74<br />
0.66<br />
0.56<br />
5.41<br />
--<br />
5.00<br />
0.63<br />
0.39<br />
0.68<br />
--<br />
1.33<br />
0.37<br />
71.74<br />
0.51<br />
0.43<br />
0.90<br />
2.00<br />
0.80<br />
0.43<br />
94.90<br />
1.51<br />
1.19<br />
1.27<br />
13.08<br />
--<br />
13.56<br />
--<br />
--<br />
0.71<br />
--<br />
1.52<br />
--<br />
52.41<br />
--<br />
--<br />
2.70<br />
0.79<br />
0.73<br />
--<br />
91.97<br />
0.11<br />
0.25<br />
1.53<br />
16.03<br />
--<br />
12.94<br />
0.18<br />
--<br />
0.37<br />
--<br />
0.96<br />
0.24<br />
57.79<br />
0.30<br />
--<br />
1.02<br />
1.07<br />
0.05<br />
0.16<br />
94.05<br />
0.18<br />
0.41<br />
--<br />
11.95<br />
--<br />
11.41<br />
--<br />
0.12<br />
0.40<br />
0.08<br />
1.03<br />
--<br />
60.11<br />
0.19<br />
--<br />
1.15<br />
2.91<br />
0.30<br />
0.11<br />
91.50<br />
0.88<br />
--<br />
1.64<br />
19.30<br />
--<br />
16.42<br />
--<br />
--<br />
--<br />
--<br />
1.61<br />
--<br />
54.29<br />
--<br />
--<br />
1.77<br />
--<br />
--<br />
--<br />
96.68<br />
0.40<br />
--<br />
0.15<br />
17.40<br />
--<br />
9.58<br />
--<br />
--<br />
0.65<br />
--<br />
1.45<br />
--<br />
63.17<br />
0.65<br />
0.11<br />
0.75<br />
1.60<br />
--<br />
0.01<br />
96.29<br />
0.60<br />
0.11<br />
0.34<br />
12.08<br />
0.41<br />
10.52<br />
0.18<br />
0.11<br />
0.25<br />
0.19<br />
1.18<br />
0.18<br />
61.29<br />
0.29<br />
0.18<br />
1.71<br />
2.45<br />
0.28<br />
0.17<br />
93.59
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table 7. Important differences in three main compounds <strong>of</strong> Origanum vulgare L. essential oil. The<br />
plants were grown with 90% Available soil moisture using fresh and saline water irrigation and/or k-<br />
humate application during three cuts in 2009 season.<br />
Compounds<br />
137<br />
Treatments<br />
Water irrigation K-humate Cuttings<br />
Mean <strong>of</strong><br />
Fresh<br />
Mean <strong>of</strong><br />
Saline<br />
Mean <strong>of</strong><br />
Without<br />
Mean <strong>of</strong><br />
With<br />
Mean <strong>of</strong><br />
Cut 1<br />
Mean <strong>of</strong><br />
Cut 2<br />
Mean <strong>of</strong><br />
Cut 3<br />
carvacrol 72.47 58.13 65.18 65.42 60.22 63.36 67.79<br />
P-cymene 8.40 14.37 11.02 12.35 13.14 13.23 8.68<br />
γ- terpinene 5.50 12.40 8.87 9.03 11.43 7.85 7.57<br />
Total 86.37 85.50 85.07 86.80 84.79 84.44 84.04<br />
Table 8. Important differences in three main compounds <strong>of</strong> Origanum vulgare L. essential oil. The<br />
plants were grown under different levels <strong>of</strong> Available soil moisture using fresh and saline water<br />
irrigation at second cut in 2009 season.<br />
Compounds<br />
Mean <strong>of</strong> 30%<br />
ASM<br />
Treatments<br />
Soil moisture Water irrigation<br />
Mean <strong>of</strong> 60%<br />
ASM<br />
Mean <strong>of</strong> 90%<br />
ASM<br />
Mean <strong>of</strong> Fresh Mean <strong>of</strong><br />
Saline<br />
carvacrol 59.19 56.80 64.87 68.49 54.08<br />
P-cymene 16.28 12.46 12.39 12.01 15.42<br />
γ- terpinene 9.64 8.96 8.25 5.94 11.96<br />
Total 85.11 78.22 85.51 86.44 81.46
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Influence <strong>of</strong> Foliar Application <strong>of</strong> Pepton on Growth, Flowering and Chemical<br />
Composition <strong>of</strong> Helichrysum bracteatum Plants under Different Irrigation<br />
Intervals.<br />
Soad , M.M. Ibrahim, Lobna, S. Taha* and M.M. Farahat<br />
Department <strong>of</strong> Ornamental Plant and Woody Trees,<br />
National Research Centre, Dokki, Cairo, Egypt<br />
*E-mail address for correspondence: lonbasalah82@yahoo.com<br />
___________________________________________________________________________________<br />
Abstract: Two field experiments were carried out at Research and Production Station, Nubaria <strong>of</strong><br />
National Research Center, Egypt, during 2007 and 2008 seasons. The purpose <strong>of</strong> this study is to<br />
investigate the influence <strong>of</strong> foliar spraying with peptone (0, 250, 500 and 1000 ppm) on growth,<br />
flowering and chemical composition under three irrigation intervals (2, 4 and 6 days) on Helichrysum<br />
bracteatum. Irrigation intervals treatments have a depressing effect on different growth characters<br />
(plant height, number <strong>of</strong> branches/plant, leaf area and fresh and dry weight <strong>of</strong> leaves) by increasing<br />
irrigation intervals. The same manner was observed and concerning flowering parameters and<br />
chemical constituents (total soluble sugars, total soluble indoles and free amino acids). On the<br />
contrary, three pigments content and total soluble phenols. Data also, showed that all growth<br />
parameters and flowering parameters (number <strong>of</strong> flower/plant, flower diameter and fresh and dry<br />
weights <strong>of</strong> flowers) were significantly promoted by increasing the concentration <strong>of</strong> pepton from 250 to<br />
500 and 1000 ppm as well as chemical constituents. The most promising results were obtained from<br />
plants treated with pepton 1000 ppm and irrigated every 2 days. These treatments may be<br />
recommended for decreasing the hazard effect on growth <strong>of</strong> Helichrysum bracteatum under different<br />
irrigation intervals.<br />
Keywords: foliar pepton, irrigation intervals, growth parameters, chemical composition.<br />
_________________________________________________________________________________<br />
INTRODUCTION<br />
Straw flower, Hardy Annual or Everlasting (Helichrysum bracteatum). Family Asteraceae is an easy<br />
annual plant to grow with yellow, orange, pink, deep rose, red, wine, magento, purplor white blooms.<br />
The true petals are found in the center <strong>of</strong> each flower and they are surrounded by colorful, straw like<br />
bracts. The flowers bloom from summer to early autumn. Harvest flowers for drying before they open<br />
fully. Seeds need light to germinate, plant in porous soil. It endemic to Austalia, growing in open<br />
scrub and grassland areas. And using in Dried Arrangement, Border, Rock garden and Cutting Bed.<br />
Water is the major component <strong>of</strong> the plant body. It constituents about 80 to 90 % <strong>of</strong> fresh weight <strong>of</strong><br />
most herbaceous plant organs and over 50 % <strong>of</strong> the fresh weight <strong>of</strong> woody parts. Water affects<br />
markedly, either directly or indirectly, most plant physiological processes. Hence, with the exception<br />
<strong>of</strong> some kinds <strong>of</strong> seeds, dehydration <strong>of</strong> plant tissues below some critical level is accompanied by<br />
irreversible changes in structure and ultimately by plant death. The importance <strong>of</strong> water in living<br />
organisms results from its unique physical and chemical properties, which also determine its functions<br />
in plant physiology, water is a major constituent <strong>of</strong> the protoplasm, it acts as a solvent for many solid<br />
and gaseous substances, forming a continuous liquid phase throughout the plant, it takes part in many<br />
important physiological reactions, it maintains cell turgor, which exerts an impact on many<br />
physiological processes. Several authors indicated the promotive effect <strong>of</strong> the high levels <strong>of</strong> wate<br />
supply on growth parameters including, Farahat (1990) on Schinus molle, Schinus terebinthifolius and<br />
Myoporum acuminatum, Sayed (2001) on Khaya senegalensis, Uday et al (2007), and Soad (2005) on<br />
143
Simmodsia chinensis, Azza and Sahar (2006)on Melia azedarach and Azza et al (2007) on Bauhinia<br />
variegata.<br />
Amino acids as organic nitrogenous compounds are the building blocks in the synthesis <strong>of</strong> proteins,<br />
Davies (1982). Amino acids are particularly important for stimulation cell growth. They act as buffers<br />
which help to maintain favorable pH value within the plant cell, since they contain both acid and basic<br />
groups; they remove the ammonia from the cell. This function is associated with amide formation, so<br />
they protect the plants from ammonia toxicity. They can serve as a source <strong>of</strong> carbon and energy, as<br />
well as protect the plants against pathogens. Amino acids also function in the synthesis <strong>of</strong> other<br />
organic compounds, such as protein, amines, purines and pyrimidiens, alkaloids vitamins, enzymes,<br />
terpenoids and others, Goss (1973) and Hass (1975), stated that the biosynthesis <strong>of</strong> cinamic acids<br />
(which are the starting materials for the synthesis <strong>of</strong> phenols) are derived from phenylalanine and<br />
tyrosine. Tyrosine is hydroxyl phenol amino acid that is used to build neurotran smitters and<br />
hormones. Several other authors indicated that promotive effect <strong>of</strong> amino acids on ornamental and<br />
medicinal plants including, Mohamed and Khalil (1992) on Antirrhinum majus, Matthiola incana and<br />
Callistephus chinensis, Hussein et al (1992) on Datura metel, Mohamed and Whaba (1993) on<br />
Rosmarinus <strong>of</strong>ficinalis, Abou Dahab and Nahed (2006) on Philodendron erubescens and Nahed and<br />
Balbaa (2007) on Saliva farinacea.<br />
Therefore, the present investigation was planned to explore the ability <strong>of</strong> helichrysum plants <strong>of</strong><br />
tolerating various degrees <strong>of</strong> drought, and possible alleviating <strong>of</strong> the harmful effects by the use <strong>of</strong><br />
pepton.<br />
MATERIALS AND METHODS<br />
Two field experiments were carried out at National Research Centre (Research and Production Station,<br />
Nubaria), during two successive seasons <strong>of</strong> 2006/2007 and 2007/2008 to investigate the effect <strong>of</strong><br />
irrigation and foliar application <strong>of</strong> peptone on growth, flowering and chemical constituents <strong>of</strong><br />
Helichrysum bracteatum plants. Helichrysum seeds were supplied from Research and Production<br />
Station, Nubaria. The soil is sand in texture with pH 8.0 , EC 0.92 dSm -1 (at 25 o C), organic carbon<br />
0.89 %, and nutrients (N % 0.036, P% 0.012, K% 0.016 and Fe 265 ppm).seeds were sown on the 1 st<br />
week <strong>of</strong> September, after 45 days from sowing uniform seedlings about 8 cm height with 2 pairs <strong>of</strong><br />
leaves were transplanted into the open field. The experiment was set up in a split plot design with three<br />
replicates (each replicate contained 6 plants) containing three treatments <strong>of</strong> irrigation intervals (2, 4 and<br />
6 days) occupied the main plots and three pepton concentrations (250, 500 and 1000 ppm) in addition<br />
to the untreated plants (control) were assigned to the subplots. The seedlings were planted in row at 50<br />
cm, distance. Drip irrigation system was applied in the experiment using drippers (4L/h) for two hours<br />
every two days. The plants were fertilized with 4g ammonium nitrate (33% N), 2g potassium sulphate<br />
(48 % K2O) and 4 g calcium super phosphate (15.5 % P2O5) / plant after 15 days from transplanting.<br />
The grown plants received the normal cultural practices during the growth seasons.<br />
Plants were sprayed with pepton (based on the energizing power <strong>of</strong> free amino acids, produced by<br />
A.P.C. Europe Co. Avsan Julain-Spain). Plants were sprayed twice with pepton until run-<strong>of</strong>f occurred;<br />
the first spraying was in the second week <strong>of</strong> March. One month later the second spray was performed.<br />
At the first week <strong>of</strong> May 2006/2007 and 2007/2008, the following data were recorded: plant height<br />
(cm), number <strong>of</strong> branches /plant, leaf area (cm 2 ) fresh and dry weights <strong>of</strong> leaves (g), number <strong>of</strong><br />
flowers/ plant, flower diameter (cm) and fresh and dry weight <strong>of</strong> flower (g). total soluble sugars were<br />
determined in the methanolic extract by using the phenol-sulphoric method according to Dubois et al<br />
(1956), photosynthetic pigments including Chlorophyll (a+b) as well as carotenoids content were<br />
determined in fresh leaves as mg/gm fresh weight, according to the procedure achieved by Saric et al<br />
(1976). The total indoles were determined in the methanolic extract, using P-dimethyl<br />
aminobenzaldhyed test " Erlic's reagent" according to Larsen et al (1962). Total soluble phenols were<br />
determined calorimetrically by using Folin Ciocalte a reagent A.O.A.C. (1985). Free amino acid<br />
content was determined according to Rosen (1957).<br />
The data were statistically analyzed for each season and then a combined analysis <strong>of</strong> the two seasons<br />
was carried out according to the procedure outlined by Steel and Torrie (1980).<br />
144
Growth parameters:<br />
RESULTS AND DISCUSSION<br />
Data presented in Table (1) indicated that significant increasing in all growth parameters by reducing<br />
the interval between irrigations. The highest values <strong>of</strong> plant height, number <strong>of</strong> branches/ plant, leaf<br />
area and fresh and dry weights <strong>of</strong> leaves were obtained at the plants irrigated every 2 days, while the<br />
lowest values occurred by irrigation at the longest intervals (6 days). Moreover, the differences<br />
between each two successive irrigation intervals were significant. Numerically, plant height and fresh<br />
weights <strong>of</strong> leaves were increased by (29.7 and 49.21%) and by (19.58 and 24.40 %) as a results <strong>of</strong> 2<br />
and 4 irrigation intervals (days), respectively, in comparison with the long interval (6 days). According<br />
to the previous results, El-Monayeri et al (1983) reported that, this may be due to the vital roles <strong>of</strong><br />
water supply at adequate amount for different physiological processes such as photosynthesis,<br />
respiration, transpiration, translocation, enzyme reaction and cells turgidity occurs simultaneously.<br />
Such reduction could be attributed to decrease in the activity <strong>of</strong> meristemic tissues responsible for<br />
elongation. As well as the inhibition photosynthesis efficiency under efficient water condition<br />
Siddique (1999). These results are in agreement with those obtained by Burman et al (1991) on<br />
Azadirachta indica, Soad (2005) on Simmondsia chinensis and Azza et (2006) on Melia azedarach.<br />
145
Table (1) Some growth parameters <strong>of</strong> Helichrysum bracteatum plants as affect with irrigation intervals and foliar application <strong>of</strong> pepton (average <strong>of</strong> two seasons).<br />
Pepton<br />
treatments<br />
(ppm)<br />
Plant height (cm) Number <strong>of</strong> branhes/plant Leaf area (cm2) Fresh weight <strong>of</strong> leaves (g) Dry weight <strong>of</strong> leaves (g)<br />
Irrigation intervals days (A)<br />
2 4 6 Mean 2 4 6 Mean 2 4 6 Mean 2 4 6 Mean 2 4 6 Mean<br />
Control 48.07 43.13 37.83 43.01 20.67 17.33 14.00 17.33 5.26 4.99 3.75 4.67 17.63 14.51 11.87 14.67 3.52 2.9 2.37 2.93<br />
P1 250 57.87 54.77 43.40 52.01 25.33 22.00 21.33 22.89 6.76 6.16 4.7 5.87 19.83 17.66 13.08 16.86 3.96 3.53 2.61 3.37<br />
P2 500 62.83 58.87 47.50 56.40 29.00 24.33 23.00 25.44 7.65 6.58 5.29 6.50 24.04 18.83 15.00 19.29 4.81 3.76 3.00 3.86<br />
P3 1000 68.7 62.10 54.30 61.70 33.33 26.33 26.33 28.66 7.72 6.70 6.18 6.87 25.82 21.80 18.59 22.07 5.16 4.36 3.71 4.41<br />
Mean 59.37 54.72 45.76 27.08 22.50 21.17 6.85 6.11 4.98 21.83 18.20 14.64 4.36 3.64 2.93<br />
LSD 5%<br />
Irrigation<br />
A<br />
1.66<br />
2.29 0.13 0.86<br />
Pepton B 1.84 1.57 0.06 0.86 0.17<br />
Interaction<br />
AB<br />
NS<br />
NS 0.11 1.49<br />
146<br />
0.17<br />
0.30
Concerning the effect <strong>of</strong> peptone on saga growth, data presented in Table (1) revealed that foliar<br />
application <strong>of</strong> peptone significantly promoted plant height, number <strong>of</strong> branches/plant, leaf area and<br />
fresh and dry weight <strong>of</strong> leaves. Increasing peptone concentration from 250 to 500 and 1000 pm to<br />
Helichrysum bracteatum plants significantly increased all growth parameters over control plants. The<br />
increments effect on plant height and number <strong>of</strong> branches/plant by (20.92, 13.13 and 43.00 %) and<br />
32.1, 46.8 and 65.54%), respectively compared with control plants. The positive effect <strong>of</strong> amino acids<br />
on yield may be due to the vital effect <strong>of</strong> these amino acids stimulation on the growth <strong>of</strong> plant cells.<br />
The positive effect <strong>of</strong> amino acids on growth was stated by Goss (1973) who indicated that amino acids<br />
can serve as a source <strong>of</strong> carbon and energy when carbohydrates become defficient in the plant, amino<br />
acids are determinate, releasing the ammonia and organic acid form which the amino acid was<br />
originally formed. The organic acids then enter the Kreb's cycle, to be broken down to release energy<br />
through respiration. Thon et al (1981) pointed out that amino acids provide plant cells with an<br />
immediately available source <strong>of</strong> nitrogen, which generally can be taken by the cells more rapidly than<br />
in organic nitrogen. The results are characteristically accompanied by Youssef et al (2004) on lemon<br />
basil, Gamal El-Din et al (1997) on lemon grass, Talaat Youssef (2002) on basil plant, El-Fawakhry<br />
and El-Tayeb (2003) on chrysanthemum, Refaat and Naguib (1998) on peppermint plant, Youssef et al<br />
(2004) on datura plant and Mona and Talaat (2005) on Pelargonium graveolens plant, the found that<br />
amino acids significantly increased vegetative growth.<br />
The interaction between different factors (irrigation and peptone ) was almost for all vegetative growth<br />
parameters except plant height and number <strong>of</strong> branches/plant. The highest values due to the irrigation<br />
regime and peptone were obtained due to irrigated every 2 days and concentration 1000 ppm <strong>of</strong> foliar<br />
spray <strong>of</strong> pepeton. The lowest sensitivity <strong>of</strong> peptone –sufficient plants to drought stress is related to the<br />
notion that some amino acids (e.g. phenylalanine, ornithine) can affect plant growth and development<br />
through their influence on gibberelline biosynthesis Waller and Nawachi (1978). Amino acids acting<br />
as the building blocks <strong>of</strong> proteins can serve in number <strong>of</strong> additional functions in regulation <strong>of</strong><br />
metabolism, transport and storage nitrogen Bidwell (1979) and Fowden (1973).<br />
Flowering Characters:<br />
Data presented in table (2) show that all decreasing irrigation intervals from 6 to 2 days significantly<br />
increased flower diameter, number <strong>of</strong> flowers/plant and fresh and dry weights <strong>of</strong> flowers. The<br />
increments on fresh and dry weights <strong>of</strong> flowers/plant by 26.93 and 31.02% respectively for the 2 days<br />
compared with 6 days. Our results are computable with those obtained by Ruhi Bastug et al (2006) on<br />
gladiolus plants, Kittas et al (2004) on Rose and Banker et al (2008) on wheat and stated that the high<br />
level <strong>of</strong> irrigation lead to the increment <strong>of</strong> flowering parameters and quality.<br />
Data presented in table (2) show that foliar spray <strong>of</strong> sage plants with pepton at 1000 ppm resulted in the<br />
highest values flowering parameters. The maximum and values were observed for number <strong>of</strong><br />
flowers/plant and fresh and dry weights <strong>of</strong> flowers/plant by 38.45, 38.51 and 38.07 %, respectively<br />
over control plants. These results are characteristically accompanied by Karima and Abd El-Wahed<br />
(2005) who found that using amino acids led to significant increases in number <strong>of</strong> flowers, diameters <strong>of</strong><br />
flower and fresh and dry weights <strong>of</strong> flowers/plant <strong>of</strong> Matricaria chamomilla L. plant. Also, Nahed<br />
and Balbaa (2007) on Saliva fFarincea stated that application <strong>of</strong> tyrosine 100 ppm significant<br />
promotion in all flowering parameters at flowering stage.<br />
Regarding the interaction effects, data in Table (2) show that flowering parameters were significantly<br />
augmented. It is also clear from the obtained data that irrigation interval 2 days combined with foliar<br />
spray <strong>of</strong> sage plants with 1000 ppm peptone resulted in the highest pronounced effects on all flowering<br />
parameters.<br />
Chemical Constituents:<br />
Pigment content<br />
Data in Table (3) recorded that, the content <strong>of</strong> three photosynthetic pigments (Chlorophyll a, b and<br />
carotenoids) were increased by the gradual increasing in irrigation intervals. Accordingly it can be<br />
stated that irrigation every 6 days was the most effective irrigation treatment for promoting the<br />
synthesis and accumulation <strong>of</strong> the three photosynthetic pigments. In harmony with these results were<br />
those obtained by Soad (2005) and Azza et al (2007).<br />
147
The three photosynthetic pigments took similar trend in response to peptone levels. The three<br />
concentrations used <strong>of</strong> peptone 250, 500 and 1000 ppm caused an increase in the contents <strong>of</strong><br />
Chlorophyll a, b and carotenoids in regard to those <strong>of</strong> untreated seedlings. Hussein et al (1992) found<br />
that higher concentration <strong>of</strong> adenine and cytosine increased the photosynthetic pigments <strong>of</strong> datura<br />
plants.<br />
148
Table (2) Flowering parameters <strong>of</strong> Helichrysum bracteatum plants as affect with irrigation intervals and foliar application <strong>of</strong> pepton (average <strong>of</strong> two seasons).<br />
Pepton<br />
treatments<br />
(ppm)<br />
Number <strong>of</strong> flowers/plant Flower diameter (cm) Fresh weight <strong>of</strong> flowers (g) Dry weight <strong>of</strong> flowers (g)<br />
Irrigation intervals days (A)<br />
2 4 6 Mean 2 4 6 Mean 2 4 6 Mean 2 4 6 Mean<br />
Control 11.83 11.30 8.83 10.65 3.23 3.13 2.17 2.84 27.20 25.96 20.32 24.49 8.70 7.79 6.09 7.53<br />
P1 250 15.63 14.23 11.13 13.66 3.32 3.48 2.75 3.18 35.96 32.74 25.61 31.44 11.50 9.82 7.68 9.67<br />
P2 500 16.60 16.00 12.50 15.03 3.76 3.56 2.87 3.40 38.18 36.54 28.75 34.49 12.21 11.06 8.63 10.63<br />
P3 1000 20.50 16.77 14.70 17.32 4.82 3.54 2.91 3.76 47.15 38.53 33.81 39.83 14.78 11.56 10.14 12.16<br />
Mean 16.14 14.58 11.79 3.78 3.43 2.68 37.12 33.44 27.12 11.80 10.06 8.14<br />
LSD 5%<br />
Irrigation<br />
A<br />
0.97 0.05 2.39 0.82<br />
Pepton B 0.51 0.04 1.12 0.39<br />
Interaction<br />
AB<br />
0.89 0.08 1.94 0.67<br />
149
Table (3) Chemical constituents <strong>of</strong> Helichrysum bracteatum plants as affect with irrigation intervals and foliar application <strong>of</strong> pepton (average <strong>of</strong> two seasons).<br />
Pepton<br />
treatments<br />
(ppm)<br />
Chl a (mg/g F.W.) Chl b (mg/g F.W.) Chl a+b (mg/g F.W.) Carotenoids (mg/g F.W.)<br />
Irrigation intervals days<br />
2 4 6 Mean 2 4 6 Mean 2 4 6 Mean 2 4 6 Mean<br />
Control 1.629 2.062 1.921 1.871 0.335 0.667 0.394 0.465 1.964 2.729 2.315 2.336 0.849 0.972 0.972 0.931<br />
P1 250 1.782 2.126 2.372 2.093 0.455 0.935 0.583 0.658 2.237 2.581 2.955 2.591 1.079 1.186 1.027 1.097<br />
P2 500 2.187 2.497 2.858 2.514 0.634 0.983 0.654 0.757 2.821 3.480 3.512 3.271 1.458 1.316 1.425 1.400<br />
P3 1000 1.851 2.444 2.750 2.348 0.524 0.976 0.614 0.705 2.375 3.420 3.364 3.053 1.269 1.634 1.286 1.396<br />
Mean 1.862 2.282 2.475 0.487 0.890 0.561 2.349 3.053 3.037 1.164 1.277 1.178<br />
LSD 5%<br />
Irrigation<br />
A<br />
0.036 0.018 0.054 0.110<br />
Pepton B 0.031 0.010 0.041 0.010<br />
Interactio<br />
n AB<br />
0.054 0.018 0.072 0.018<br />
150
The present data are in agreement with the findings <strong>of</strong> Hussein (2003) on Foeniculum vulgare L. plants<br />
and Nahed and Laila (2007) on Saliva farinacea plants, they reported that foliar application <strong>of</strong> amino<br />
acids (Tryptophan) caused an increase in photosynthetic pigments contents. The accumulation <strong>of</strong><br />
photosynthetic pigments as a result <strong>of</strong> these nitrogen compounds may be due to the important role <strong>of</strong><br />
nitrogen in the biosynthesis <strong>of</strong> Chlorophyll molecules, Meyeret et al (1968).<br />
In this respect, interaction between irrigation intervals and pepton applications, the data revealed that<br />
the combination <strong>of</strong> both factors on Chlorophyll a, b and carotenoids was more effective than the effect<br />
<strong>of</strong> each factors, all the interaction <strong>of</strong> used treatments increased significantly photosynthetic pigments in<br />
the leaves <strong>of</strong> Helichrysum bracteatum plants.<br />
Total soluble sugars content:<br />
Data recorded in Table (4) indicated that total soluble sugars content as affected by different irrigation<br />
intervals treatments, followed the same manner obtained previously on photosynthetic pigments, were<br />
gradually decreased by increasing the intervals <strong>of</strong> irrigation. These results were in accordance with<br />
those recorded by Azza et al (2007).<br />
Pepton at all used concentration caused an increasing in total soluble sugars content as compared with<br />
untreated seedlings. This result could be explained by the findings obtained by Refaat and Naguib<br />
(1998) reported that application <strong>of</strong> all amino acids (alanine, cytosine, guanine, thiamine and L-tyrosine)<br />
increased the total carbohydrates percentage in peppermint leaves. The promotive affected <strong>of</strong> the<br />
amino acids on the total carbohydrates content may be due to their important role on the biosynthesis <strong>of</strong><br />
Chlorophyll molecules which in turn affected carbohydrate content.<br />
As far the interaction between irrigation intervals and peptone applications the higher values were<br />
provided when adding 1000 ppm peptone and irrigation every 4 days.<br />
Total soluble indoles:<br />
According to the data illustrated in Table (4) the total indoles levels which were determined in leaves<br />
<strong>of</strong> Helichrysum bracteatum plants were increased by decreasing irrigation intervals.<br />
Concerning pepton, total indoles levels were decreased by the increase in peptone levels. The highest<br />
values <strong>of</strong> total indoles were obtained from interaction treated plants with peptone at 1000 ppm and<br />
irrigated every 4 days.<br />
151
Table (4) Chemical constituents <strong>of</strong> Helichrysum bracteatum plants as affect with irrigation intervals and foliar application <strong>of</strong> pepton (average <strong>of</strong> two seasons).<br />
Pepton treatments<br />
(ppm)<br />
Total soluble sugars (mg/g F.W.) Total indoles (mg/g F.W.) Total phenoles (mg/g F.W.)<br />
Irrigation intervals days<br />
152<br />
Total free amino acids (mg/g<br />
F.W.)<br />
2 4 6 Mean 2 4 6 Mean 2 4 6 Mean 2 4 6 Mean<br />
Control 0.948 2.245 1.338 1.510 1.225 1.117 1.292 1.211 1.165 1.354 0.908 1.142 0.971 0.685 0.714 0.790<br />
P1 250 1.659 3.143 1.511 2.104 0.816 0.718 0.635 0.723 1.216 1.659 1.510 1.462 1.132 0.835 0.742 0.903<br />
P2 500 1.983 3.459 1.941 2.461 1.184 0.966 0.784 0.978 1.242 1.733 1.535 1.503 1.242 1.027 0.814 1.028<br />
P3 1000 2.045 3.580 2.865 2.830 1.246 0.482 0.813 0.847 1.364 2.506 1.594 1.821 1.375 1.091 0.910 1.125<br />
Mean 1.659 3.107 1.914 1.118 0.821 0.881 1.247 1.813 1.387 1.180 0.910 0.795<br />
LSD 5%<br />
Irrigation<br />
A<br />
0.018 0.009 0.008 0.007<br />
Pepton B 0.013 0.008 0.010 0.008<br />
Interaction<br />
AB<br />
0.022 0.014 0.018 0.013
Total soluble phenols:<br />
The results in Table (4) emphasized that amounts <strong>of</strong> total soluble phenols were significantly increased<br />
by increasing irrigation intervals. These results are in accordance with those obtained by Azza et al<br />
(2006) on Taxodium distichum. Concerning peptone, total soluble phenols levels were increased by<br />
increasing irrigation intervals and peptone concentration the highest values were provided when adding<br />
1000 ppm and interval 4 days.<br />
Total free amino acids:<br />
From the given data in Table (4) it can be concluded that decreasing irrigation intervals caused an<br />
increase <strong>of</strong> total free amino acids content. In regard to the effect <strong>of</strong> water stress on amino acids, it has<br />
been indicated that generally total free amino acids increased under water stress, Simpson (1981). This<br />
trend does not apply to Myoporum since long irrigation interval caused a decrease in amino acids.<br />
However, many investigators reported that an increase in amino acids is associated with water stress,<br />
Farahat (1990) on Schinus molle, Schinus terebinthifolius and Myoporum acuminatum). Data<br />
presented in table (4) show that total free amino was significantly increased as a result <strong>of</strong> foliar spray <strong>of</strong><br />
peptone 500 and 1000 ppm. Our results are in agreement with those obtained by Karima and Abdel-<br />
Wahed (2005) on Chamomile plants, Gamal ElDin et al (1997) on lemon grass, Mona and Iman (2005)<br />
on Pelargonium graveolens L. and Nahed and Balbaa (2007) on Saliva fariacea plants. They reported<br />
that application <strong>of</strong> amino acids significantly increased total amino acids.<br />
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155
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Permeability and Porosity Prediction from Wireline logs Using Neuro-Fuzzy Technique<br />
Wafaa El-Shahat Afify* and Alaa H. Ibrahim Hassan**<br />
*Lecturer <strong>of</strong> <strong>Applied</strong> Geophysics, Faculty <strong>of</strong> <strong>Science</strong>, Benha University<br />
** Senior Reservoir Geologist (Bab Team)<br />
Abu Dhabi Company for Onshore Oil Operations<br />
*E-mail address for correspondence: w_afify@yahoo.com<br />
____________________________________________________________________________________<br />
Abstract: Petroleum reservoir characterization is a process for quantitatively describing various<br />
reservoir properties in spatial variability using all the available field data. Porosity and permeability are the<br />
two fundamental reservoir properties which relate to the amount <strong>of</strong> fluid contained in a reservoir and its<br />
ability to flow. These properties have a significant impact on petroleum fields operations and reservoir<br />
management. In un-cored intervals and well <strong>of</strong> heterogeneous formation, porosity and permeability<br />
estimation from conventional well logs has a difficult and complex problem to solve by statistical methods.<br />
This paper suggests an intelligent technique using fuzzy logic and neural network to determine reservoir<br />
properties from well logs. Fuzzy curve analysis based on fuzzy logic is used for selecting the best related<br />
well logs with core porosity and permeability data. Neural network is used as a nonlinear regression<br />
method to develop transformation between the selected well logs and core measurements. The technique is<br />
demonstrated with an application to the well data in West July oil field, Gulf <strong>of</strong> Suez, Egypt for the<br />
Miocene Upper Rudeis reservoirs (Asal and Hawara formations). The results show that the technique can<br />
make more accurate and reliable reservoir properties estimation compared with conventional computing<br />
methods. This intelligent technique can be utilized as a powerful tool for reservoir properties estimation<br />
from well logs in oil and natural gas development projects.<br />
____________________________________________________________________________________<br />
INTRODUCTION<br />
Reservoir characterization is a process <strong>of</strong> describing various reservoir characteristics using all the<br />
available data to provide reliable reservoir models for accurate reservoir performance prediction. The<br />
reservoir characteristics include permeability, porosity, pore and grain size distributions, facies distribution,<br />
and depositional environment. The types <strong>of</strong> data needed for describing the characteristics are core data,<br />
well logs, well tests, production data and seismic survey. Such information is essential to the determination<br />
<strong>of</strong> the economic viability <strong>of</strong> a particular well or reservoir to be explored. A large number <strong>of</strong> techniques<br />
have been introduced in order to establish an adequate interpretation model over the past fifty years.<br />
Nevertheless, conventional derivation <strong>of</strong> a well log data analysis model normally falls into one <strong>of</strong> the two<br />
main approaches: empirical and statistical. In the empirical approach, mathematical functions relating the<br />
desired permeability based on several well log data inspired by theoretical concepts are used [Wyllie and<br />
Rose, 1950, Kapadia and Menzie, 1985]. This approach has long been favored in the field and much effort<br />
has been made to understand the underlying petroleum engineering principles. However, the unique<br />
geophysical characteristic <strong>of</strong> each region prevents a single formula from being universally applicable.<br />
Statistical techniques are viewed as more practical approaches [Wendt et al., 1986, and Hawkins, 1994].<br />
The common statistical technique used is multiple regression analysis. The simplest form <strong>of</strong> regression<br />
analysis is to find a relationship between the input logs and the petrophysical properties. The derived<br />
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regression equations are then used for well log analysis. However, a number <strong>of</strong> initial assumptions <strong>of</strong> the<br />
model need to be made. Assumptions must also be made as to the statistical characteristics <strong>of</strong> the log data.<br />
Over the past decade, another technique that has emerged as an option for well log analysis is the Artificial<br />
Neural Network (ANN). Research has shown that an ANN can provide an alternative approach to well log<br />
analysis with improvement over the traditional methods [Osborne, 1992, Wong et al., 1995, Fung and<br />
Wong, 1999]. Most <strong>of</strong> the ANN based well log analysis models have used the Multi-layer Neural Network<br />
(MLNN) utilizing the backpropagation learning algorithm. Such networks are commonly known as<br />
Backpropagation Neural Networks (BPNNs). A BPNN is suited to this application, as it resembles the<br />
characteristics <strong>of</strong> regression analysis in statistical approaches. Fuzzy Logic (FL) that is capable to express<br />
the underlying characteristics <strong>of</strong> a system in human understandable rules is also used. A fuzzy set allows<br />
for the degree <strong>of</strong> membership <strong>of</strong> an item in a set to be any real number between 0 and 1. This allows human<br />
observations, expressions and expertise to be modeled more closely. Once the fuzzy sets have been defined,<br />
it is possible to use them in constructing rules for fuzzy expert systems and in performing fuzzy inference.<br />
This approach seems to be suitable to well log analysis as it allows the incorporation <strong>of</strong> intelligent and<br />
human knowledge to deal with each individual case. However, the extraction <strong>of</strong> fuzzy rules from the data<br />
can be difficult for analysts with little experience. This could be a major drawback for use in well log<br />
analysis. If a fuzzy rule extraction technique is made available, then fuzzy systems can still be used for well<br />
log analysis [Wong et al., 1999 and Kuo et al., 1999]. With the emergence <strong>of</strong> intelligent techniques that<br />
combine ANN and fuzzy together have been applied successfully in well log analysis [Huang et al., 2001,<br />
Kadkhodaie Ilkhchi et al., 2008, Khaxar et al., 2007, Johanyák et al.2007]. These techniques used in<br />
building the well log analysis model normally address the disadvantages encountered in ANN and fuzzy<br />
system. This paper suggests an intelligent technique for reservoir characterization using fuzzy logic and<br />
neural network to determine reservoir properties from well log data for the Miocene Upper Rudeis<br />
reservoirs (Asal and Hawara formations), in West July oil field, Gulf <strong>of</strong> Suez, Egypt, Fig.1.<br />
Back propagation neural networks (BPNN).<br />
A neural network (NN) is an intelligent tool for solving complex problems. A BPNN is a supervised<br />
training technique that sends the input values forward through the network then computes the difference<br />
between calculated output and corresponding desired output from the training dataset. The error is then<br />
propagated backward through the net and the weights are adjusted during a number <strong>of</strong> iterations, named<br />
epochs. The training ceases when the calculated output values best approximate the desired values [Bhatt<br />
and Helle, 2002].A flowchart <strong>of</strong> training procedure in a supervised NN is shown in Fig. 2.<br />
Fuzzy logic (FL).<br />
The basic theory <strong>of</strong> fuzzy sets was first introduced by Zadeh, 1965. In recent years, it has been shown that<br />
uncertainty may be due to fuzziness (possibility) rather than probability. FL is considered to be appropriate<br />
to deal with the nature <strong>of</strong> uncertainty in system and human errors, which were not considered in existing<br />
reliability theories. Generally, geological data are not clear-cut and habitually are associated with<br />
uncertainties. For example, prediction <strong>of</strong> core parameters from well log responses is difficult and is usually<br />
associated with error [Nikravesh and Aminzadeh, 2003].FL derives useful information from this error and<br />
applies it as a powerful parameter for increasing the accuracy <strong>of</strong> the predictions. A fuzzy inference system<br />
(FIS) is a method to formulate inputs to an output using FL [Kadkhodaie Ilkhchi et al., 2006].<br />
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Fig.2. A flow chart <strong>of</strong> training procedure in a supervised<br />
neural network.<br />
Fuzzy modeling technique can be classified into three categories, namely the linguistic (Mamdani-type), the<br />
relational equation, and the Takagi, Sugeno and Kang (TSK). Takagi and Sugeno, 1985, is a FIS in which<br />
output membership functions are constant or linear and are extracted by a clustering process. Each <strong>of</strong> these<br />
clusters refers to a membership function. Each membership function generates a set <strong>of</strong> fuzzy if–then rules<br />
for formulating inputs to outputs. A schematic diagram <strong>of</strong> FIS is shown in Fig.3.<br />
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Neuro-fuzzy (NF) model.<br />
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Hybrid NF systems combine the advantages <strong>of</strong> fuzzy systems (which deal with explicit knowledge) with<br />
those <strong>of</strong> NN (which deal with implicit knowledge). On the other hand, Fuzzy Logic (FL) enhances<br />
generalization capability <strong>of</strong> a Neural Network (NN) system by providing more reliable output when<br />
extrapolation is needed beyond the limits <strong>of</strong> the training data. A schematic diagram <strong>of</strong> information flows in<br />
a NF system is shown in Fig.4. The architecture <strong>of</strong> the Neuro-Fuzzy classifier is slightly different from the<br />
architecture used in function approximations [Tommi, 1994]. The two first layers have the identical<br />
function with the approximation. Fig. 5 shows a system using the following fuzzy rules,<br />
Rule 1: If x1 is A1 and x2 is B1, then class is 1.<br />
Rule 2: If x1 is A2 and x2 is B2, then class is 2.<br />
Rule 3: If x1 is A1 and x2 is B3, then class is 1.<br />
Layer 3. Combination <strong>of</strong> firing strengths: If several fuzzy rules have the same consequence class, this layer<br />
combines their firing strengths. Usually, the maximum connective (or operation) is used.<br />
Layer 4. Fuzzy outputs: In this layer, the fuzzy values <strong>of</strong> the classes are available. The values describe how<br />
well the input <strong>of</strong> the system matches to the classes.<br />
Layer 5. Defuzzification: If the crisp classification is needed, the best-matching class for the input is chosen<br />
as output class.<br />
METHODS AND RESULTS<br />
The data used for permeability and porosity determination are the open-hole wireline subsurface well log<br />
data [gamma ray (GR), sonic (DT), density (ROHB), deep resistivity (RD), Neutron (PHIN) logs, water<br />
saturation (SW)], and core data [core permeability and core porosity]. The work in the present research<br />
proceeds as following;<br />
• Removing erroneous and outliers from the raw well log data.<br />
• Organizing data into input data sets including GR, DT, ROHB, RD, PHIN, SW and<br />
output data sets including core permeability and core porosity.<br />
• Normalization <strong>of</strong> input and output data sets (between the ranges 0-1) to renders the data<br />
dimensionless and removes the effect <strong>of</strong> scaling.<br />
• Dividing the data into: training, checking and testing data sets.<br />
• Clustering the input and output data sets using fuzzy c-means (FCM), fuzzy k-means<br />
(FKM) or subtractive clustering methods.<br />
• Fuzzyfication, which involves the conversion <strong>of</strong> numeric data in real world domain to<br />
fuzzy numbers in fuzzy domain, this takes place by building the fuzzy inference system<br />
FIS, which involves setting the membership functions and establishment <strong>of</strong> fuzzy rules.<br />
• Deffuzzification, which is optional, involves the conversion <strong>of</strong> the derived fuzzy<br />
number to the numeric data in real world domain.<br />
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Fig.3. Schematic diagram <strong>of</strong> FIS<br />
Fig.4. Schematic diagram <strong>of</strong> information flow in a NF system<br />
Fig.5. Neural architecture <strong>of</strong> the NF classifier.<br />
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•Organizing data. The data for the neuro-fuzzy model come from one well SG-3105A at West July oil<br />
field, Gulf <strong>of</strong> Suez, Egypt. The selection <strong>of</strong> this well is based on geological considerations; it contains<br />
reasonably good core coverage <strong>of</strong> the Upper Rudeis Formation. Core-log calibration was carefully carried<br />
out to compensate for differences in depth. Table (1), illustrates the statistics <strong>of</strong> the input and output data<br />
sets used in NF modeling.<br />
•Normalizing data. When processing the actual materials, due to the different dimensions <strong>of</strong> the source<br />
rocks evaluation parameter, the volume level <strong>of</strong> actual data vary considerably. If we calculate by using the<br />
raw data directly, the indicating role <strong>of</strong> the data which has a larger volume would become more<br />
outstanding. While the indicator with a lower volume and a higher sensitivity will be underestimated. Thus,<br />
we should preprocess and normalize the raw data. In this work normalizing data takes place by using the<br />
maximum and minimum values <strong>of</strong> the data.<br />
•Fuzzy clustering. It is necessary to classify the input and output datasets into groups using clustering<br />
methods. In this study, a subtractive clustering method, which is a useful and effective way to FL modeling,<br />
is used for extraction <strong>of</strong> clusters and fuzzy if–then rules. The details <strong>of</strong> subtractive clustering could be<br />
found in Chiu [1994], Chen and Wang [1999], Jarrah and Halawani [2001].The important parameter in<br />
subtractive clustering which controls number <strong>of</strong> clusters and fuzzy if–then rules is clustering radius. This<br />
parameter could take values between the range <strong>of</strong> [0, 1]. Specifying a smaller cluster (say 0.1) radius will<br />
usually yield more and smaller clusters in the data resulting in more rules. In contrast, a large cluster radius<br />
(say 0.9) yields a few large clusters in the data resulting in few rules.<br />
The effectiveness <strong>of</strong> a fuzzy model is related to the search for an optimal clustering radius, which is a<br />
controlling parameter for determining the number <strong>of</strong> fuzzy if–then rules. Few rules could not cover the<br />
entire domains, and more rules will complicate the system behavior and may lead to low performance <strong>of</strong><br />
the model. Regarding the permeability model, four centers result from clustering, thus the fuzzy model was<br />
established by four fuzzy if-then rules and four membership functions for input and output data. Porosity<br />
model, on the other hand, contains five centers (clusters), five rules and five membership functions. Figures<br />
6 and 7 shows the subtractive clusters <strong>of</strong> permeability and porosity data.<br />
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•Building the fuzzy inference system FIS. Fuzzy inference is the process <strong>of</strong> formulating the mapping from<br />
a given input to an output using fuzzy logic. The mapping then provides a basis from which decisions can<br />
be made, or patterns discerned. The process <strong>of</strong> fuzzy inference involves setting the membership functions<br />
and establishment <strong>of</strong> fuzzy rules, [Matlab fuzzy logic user’s guide, and 2009].<br />
1- Setting the Membership Functions (MF). A membership function (MF) is a curve that defines how each<br />
point in the input space is mapped to a membership value (or degree <strong>of</strong> membership) between 0 and 1. The<br />
input space is sometimes referred to as the universe <strong>of</strong> discourse, a fancy name for a simple concept. The<br />
only condition a membership function must really satisfy is that it must vary between 0 and 1. The function<br />
itself can be an arbitrary curve whose shape we can define as a function that suits us from the point <strong>of</strong> view<br />
<strong>of</strong> simplicity, convenience, speed, and efficiency. There are many types <strong>of</strong> membership functions built<br />
from several basic functions:<br />
• Piece-wise linear functions<br />
• The Gaussian distribution function<br />
• The sigmoid curve<br />
• Quadratic and cubic polynomial curves<br />
In this study, a Gaussian distribution membership function is used to define the extracted input clusters. A<br />
Gaussian function f (x) shows the normal distribution <strong>of</strong> data (x):<br />
e<br />
f ( X ) �<br />
�<br />
�(<br />
x��<br />
)<br />
2 /<br />
�<br />
2�<br />
2<br />
Where µ and σ are the parameters <strong>of</strong> normal distribution showing the mean and standard deviation <strong>of</strong> data,<br />
respectively. These Gaussian membership functions are constructed from mean and σ values <strong>of</strong> the clusters.<br />
The mean represents the cluster centers and σ is derived from:<br />
σ = (radii � (maximum data – minimum data))/sqrt. The input parameters <strong>of</strong> Gaussian membership<br />
function for permeability and porosity are shown in tables 2A and 3A.<br />
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In the FIS, output membership functions are linear equations constructed from inputs. For example, output<br />
membership function number one (MF1), which is the consequent <strong>of</strong> rule no. 1, is constructed from six<br />
petrophysical inputs as following:<br />
Output MF1 = C1 � GR � C2<br />
� DT � C3<br />
� ROHB � C4<br />
� RD � C5<br />
� PHIN � C6<br />
� SW � C7<br />
In this equation, parameters C 1 , C2,<br />
C3,<br />
C4,<br />
C5<br />
and C 6 are coefficients corresponding to GR, DT,<br />
ROHB, RD, PHIN and SW inputs, respectively. Parameter C 7 is constant in each equation. These<br />
parameters are obtained by linear least-squares estimation. With these explanations there will be seven<br />
parameters for each output membership function, which are shown in tables 2B and 3B for permeability<br />
and porosity, respectively. Figures 8 and 9 represent the FIS generated Gaussian membership<br />
functions <strong>of</strong> input data for permeability and porosity model, respectively.<br />
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Moreover, Figure 10 A shows the FIS model generated for permeability and porosity, (Fig.10B).<br />
2- Establishment <strong>of</strong> fuzzy rules. Fuzzy rule statements are used to formulate the conditional statements that<br />
comprise fuzzy logic. A single fuzzy if-then rule assumes the form if x is A then y is B where A and B are<br />
linguistic values defined by fuzzy sets on the ranges (universes <strong>of</strong> discourse) X and Y, respectively. The ifpart<br />
<strong>of</strong> the rule “x is A” is called the antecedent or premise, while the then-part <strong>of</strong> the rule “y is B” is called<br />
the consequent or conclusion.<br />
The generated fuzzy if-then rules for formulating input petrophysical data to permeability are:<br />
1. If (GR is in1mf1) and (DT is in2mf1) and (ROHB is in3mf1) and (RD is in4mf1) and (PHIN is in5mf1)<br />
and (SW is in6mf1) then (K is out1mf1).<br />
2. If (GR is in1mf2) and (DT is in2mf2) and (ROHB is in3mf2) and (RD is in4mf2) and (PHIN is in5mf2)<br />
and (SW is in6mf2) then (K is out1mf2).<br />
3. If (GR is in1mf3) and (DT is in2mf3) and (ROHB is in3mf3) and (RD is in4mf3) and (PHIN is in5mf3)<br />
and (SW is in6mf3) then (K is out1mf3).<br />
4. If (GR is in1mf4) and (DT is in2mf4) and (ROHB is in3mf4) and (RD is in4mf4) and (PHIN is in5mf4)<br />
and (SW is in6mf4) then (K is out1mf4).<br />
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The generated fuzzy if-then rules for formulating input petrophysical data to porosity are:<br />
1. If (GR is in1mf1) and (DT is in2mf1) and (ROHB is in3mf1) and (RD is in4mf1) and (PHIN is in5mf1)<br />
and (SW is in6mf1) then (PHI is out1mf1).<br />
2. If (GR is in1mf2) and (DT is in2mf2) and (ROHB is in3mf2) and (RD is in4mf2) and (PHIN is in5mf2)<br />
and (SW is in6mf2) then (PHI is out1mf2).<br />
3. If (GR is in1mf3) and (DT is in2mf3) and (ROHB is in3mf3) and (RD is<br />
in4mf3) and (PHIN is in5mf3) and (SW is in6mf3) then (PHI is out1mf3).<br />
4. If (GR is in1mf4) and (DT is in2mf4) and (ROHB is in3mf4) and (RD is in4mf4) and (PHIN is in5mf4)<br />
and (SW is in6mf4) then (PHI is out1mf4).<br />
5. If (GR is in1mf5) and (DT is in2mf5) and (ROHB is in3mf5) and (RD is in4mf5) and (PHIN is in5mf5)<br />
and (SW is in6mf5) then (PHI is out1mf5).<br />
A graphical illustration showing steps to formulation <strong>of</strong> petrophysical data inputs to permeability using four<br />
fuzzy if–then rules generated by FIS, is represented in Fig.11. The formulation <strong>of</strong> petrophysical data to<br />
porosity using five fuzzy if-then rules generated by FIS are shown in Fig. 12. Each figure displays a<br />
roadmap <strong>of</strong> the whole fuzzy inference process. The seven plots across the top <strong>of</strong> the figure represent the<br />
antecedent and consequent <strong>of</strong> the first rule. Each rule is a row <strong>of</strong> plots, and each column is a variable. The<br />
rule numbers are displayed on the left <strong>of</strong> each row.<br />
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The structure <strong>of</strong> the NF model is now generated for permeability (Fig.13A) and porosity (Fig.13B). The<br />
input is represented by the left-most node and the output by the right-most node. The node represents a<br />
normalization factor for the rules.<br />
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DISCUSSION<br />
The NF technique is used to determine the porosity and permeability <strong>of</strong> the Upper Rudeis Formation using<br />
the available well data, as well as core permeability and core porosity data, (Fig. 14). The Upper Rudeis<br />
sand is the third most important reservoir in July oil field. The sand was supplied by fans draining the Red<br />
Sea hills to the west <strong>of</strong> July field and deposited in a similar environment to the Lower Rudeis Formation,<br />
Pivnik et al., (2003).<br />
A total <strong>of</strong> 108 data points are used for training, 108 data points are used for checking and 60 data points are<br />
used for testing the NF models <strong>of</strong> the permeability and porosity. The FIS is trained using the training data<br />
set then checked and tested using checking data sets and testing data sets respectively. The testing data set<br />
is used to check the generalization capability <strong>of</strong> the resulting fuzzy inference system. The idea behind using<br />
a checking data set for model validation is that after a certain point in the training, the model begins over<br />
fitting the training data set. In principle, the model error for the checking data set tends to decrease as the<br />
training takes place up to the point that over fitting begins, and then the model error for the checking data<br />
suddenly increases. Over fitting is accounted for by testing the FIS trained on the training data against the<br />
checking data. Usually, these training and checking data sets are collected based on observations <strong>of</strong> the<br />
target system and are then stored in separate files.<br />
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Figure 15 shows the checking and the FIS output. On the other hand, Fig.16. shows testing data and FIS<br />
output. The performance <strong>of</strong> the model is evaluated by the MSE <strong>of</strong> the data sets, as illustrated in Fig.17. and<br />
table (4). The correlation coefficient between the measured and NF predicted K and PHI are 0.825 and<br />
0.957, respectively. A comparison between measured and NF predicted K and PHI versus depth is shown in<br />
Figs. 18 and 19.<br />
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CONCLUSIONS<br />
In this study, the NF intelligent technique is used to estimate reservoir porosity and permeability from<br />
conventional well logs. Fuzzy curve analysis based on fuzzy logic can be used for selecting the<br />
best related parameters with reservoir properties. The NF modeling approach presented in this paper has<br />
been successfully applied for the prediction <strong>of</strong> petrophysical reservoir parameters. This modeling approach<br />
has the significant advantage in that it does not require any previous assumption based on physical or<br />
experimental considerations about the reservoir complexities to construct a reasonable and accurate model<br />
from a set <strong>of</strong> measured data. Excellent correlation coefficients have been obtained for porosity 0.957, and<br />
permeability 0.825, using NF models. The techniques can make more accurate and reliable reservoir<br />
properties estimation and can be utilized a powerful tool for reservoir properties determination from well<br />
logs in petroleum industry, and is applicable in different wells and oil fields.<br />
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ACKNOWLEDGEMENTS<br />
The authors would like to express their gratitude for the Gulf Of Suez Petroleum Company, (GUPCO),<br />
Egypt for supplying the data needed for this work.<br />
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Kadkhodaie Ilkhchi, A., Hossain Rahimpour-Bonab, and Rezaee, M.R., 2008. A committee machine with<br />
intelligent systems for estimation <strong>of</strong> total organic carbon content from petrophysical data: An<br />
example from Kangan and Dalan reservoirs in South Pars Gas Field, Iran <strong>Journal</strong> <strong>of</strong> Computers<br />
and Geosciences, doi:10.1016/j.cageo.2007.12.007<br />
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<strong>Journal</strong>, 28, pp. 80-83.<br />
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Egypt, AAPG Bulletin, v. 87, pp. 1015-1030.<br />
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174
Figure 1 - Location map <strong>of</strong> July Oil Field.<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
FIGURES CAPTION<br />
Figure 2 - A flow chart <strong>of</strong> training procedure in a supervised neural network.<br />
Figure 3 - Schematic diagram <strong>of</strong> FIS.<br />
Figure 4 - Schematic diagram <strong>of</strong> information flow in a NF system.<br />
Figure 5 - Neural architecture <strong>of</strong> the NF classifier.<br />
Figure 6 - Subtractive clustering <strong>of</strong> permeability fuzzy model.<br />
Figure 7 - Subtractive clustering <strong>of</strong> porosity fuzzy model.<br />
Figure 8 - Generated Gaussian membership functions for permeability model input data.<br />
Figure 9 - Generated Gaussian membership functions for porosity model input data.<br />
Figure 10 - Diagrams showing formulation <strong>of</strong> input petrophysical data to: (A)<br />
permeability, K and (B) porosity, PHI using fuzzy modeling.<br />
Figure 11 – Rule viewer <strong>of</strong> FIS permeability model.<br />
Figure 12 - Rule viewer <strong>of</strong> FIS porosity model.<br />
Figure 13 - Structure <strong>of</strong> Neuro-Fuzzy model for permeability (A) and porosity (B).<br />
Figure 14 - Petrophysical and core data <strong>of</strong> SG-310-5A well.<br />
Figure 15 - Showing checking data and FIS output, permeability (A) and porosity (B).<br />
Figure 16 - Showing testing data and FIS output, permeability (A) and porosity (B).<br />
Figure 17 - Mean square error (MSE) obtained during training the permeability<br />
model (A) and the porosity model (B).<br />
Figure 18 - Predicted and core permeability.<br />
Figure 19 - Predicted and core porosity.<br />
TABLES CAPTION<br />
Table1 - Statistics <strong>of</strong> input and output data sets.<br />
Table 2 - Showing input (a) and output (b) membership functions parameters derived by<br />
FIS for permeability.<br />
Table 3 - Showing input (a) and output (b) membership functions parameters derived by<br />
FIS for porosity.<br />
Table 4 - MSE <strong>of</strong> the different datasets.<br />
175
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
Response <strong>of</strong> vegetative growth and chemical constituents <strong>of</strong> Schefflera<br />
arboricola L. plant to foliar application <strong>of</strong> inorganic fertilizer (grow-more)<br />
and ammonium nitrate at Nubaria.<br />
Mona, H. Mahgoub *, El-Quesni, Fatma E.M., and Magda,M. Kandil<br />
Department <strong>of</strong> Ornamental plant and Woody trees,<br />
National Research Centre, Dokki, Cairo, Egypt<br />
*E-mail address for correspondence: azza856@yahoo.com<br />
________________________________________________________________________________<br />
Abstract: A pot experiment was carried out during 2007 and 2008 seasons at Research and Production<br />
Station, Nubaria <strong>of</strong> National Research Centre, Dokki, Cairo, Egypt to study the response <strong>of</strong> Schefflera<br />
plants to foliar fertilizer (Grow-more at the rates <strong>of</strong> 0.0, 1.0 cm 3 /L and 2.0 cm 3 /L) and ammonium<br />
nitrate at the rate <strong>of</strong> (0, 100 and 200 kg) and their interaction on vegetative growth expressed as plant<br />
height, stem diameter, number <strong>of</strong> leaves, leaf area, fresh and dry weight <strong>of</strong> (leaves, roots and stem) and<br />
chemical composition significantly affected by application <strong>of</strong> the two factors which were used in this<br />
study.Grow-more and nitrogen fertilizer promoted all morphological characters, photosynthetic<br />
pigments, protein %, nitrogen, phosphorus and potassium.,<br />
Keywords: Schefflera arboricola,Grow-more,ammonium nitrate<br />
__________________________________________________________________________________<br />
INTRODUCTION<br />
Schefflera arboricola L. is flowering plant in the family araliaceae, native to Tiwan and Hainan. It is<br />
also goes by the common name "Dwarf umbrella tree". It is an evergreen shrub growing to 3-4 m<br />
height, <strong>of</strong>ten trailing stems scrambing over other vegetation. The leaves are palmately compound, with<br />
7-9 leaflets, the leaflets 9-20 cm long and 4-10 cm broad (though <strong>of</strong>ten smaller in cultivation). The<br />
flowers are produced in a 20 cm pancil <strong>of</strong> small umbels, each umbel 7-10 mm diameter with 5-10<br />
flowers.<br />
It is commonly grown as houseplant, popular for its tolerance <strong>of</strong> neglect and poor growing condition.<br />
Numerous cultivars have been selected for variation in leaf colour and pattern, <strong>of</strong>ten variegated with<br />
creamy-white to yellow edges or centers, and dwarf forms. Scheffleras are delicate tropical plants<br />
<strong>of</strong>ten used to decorate public places, such as lobbies, shopping malls and waiting rooms. Smaller<br />
Scheffleras are better studied for homes and small <strong>of</strong>fices. Uph<strong>of</strong>(1959). Inorganic fertilizers are the<br />
elements needed in small amounts, they are <strong>of</strong>ten refers to as micronutrients (Kohnke 1995) these<br />
elements are chlorine (Cl), Iron (Fe), Manganese (Mg), Boron (B), Copper (Cu), Zinc (Zn),<br />
Molybdenum (Mo), Nickel (Ni) and Cobalt (Co) most <strong>of</strong> these elements are derived from the soil and<br />
organic sources (Brady and Weil 2000). Micronutrients are also essential for organization and rapid<br />
alternation <strong>of</strong> nutrition compound within plant owing to their great importance in contribution to direct<br />
the enzymes way in metabolism Massoud et al (2005). Therefore, both granular and fluid (liquid) NPK<br />
fertilizers are commonly used as carriers <strong>of</strong> micronutrients including micronutrients with mixed<br />
fertilizer which is a convenient method <strong>of</strong> application and allows more uniform distribution with<br />
conventional application equipment. Micronutrients are essential for plant growth, but are required in<br />
much smaller amounts than those <strong>of</strong> the primary nutrients Brady and Weil (2000).<br />
Nitrate and ammonium are the major source <strong>of</strong> inorganic nitrogen taken up by the roots <strong>of</strong> higher<br />
plants. Most <strong>of</strong> ammonium has to be incorporated into organic compounds in the roots whereas nitrate<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
is readily mobile in the xylem and can also be stored in the vacules <strong>of</strong> roots, shoots and storage organs.<br />
Nitrate accumulation can be considerable importance for cation-anion balance, for osmoregulation,<br />
particularly in so-called nitrophilie species such as Chenopodium album and Urtica dioica (Smirn<strong>of</strong>f<br />
and Stewart, 1985). Dahiya et al (2001) mentioned that further increments in nitrogen level, up to 180<br />
ppm, adversely affected growth and dry matter yield <strong>of</strong> tuberose. While Pal and Biswas (2000) found<br />
that the lower doses <strong>of</strong> fertilizer produced poor quality plant and yield <strong>of</strong> flower and best results were<br />
found when tuberose were fertilized N, P and K at the level <strong>of</strong> 15, 15, 20 g/m 2 , respectively. Also<br />
Paradhan et al (2004) noticed that combined application <strong>of</strong> N at 40 g/m 2 and K at 30 g/m 2 gave the<br />
highest values <strong>of</strong> plant height, number <strong>of</strong> leaves /plant, leaf area, spike length and number <strong>of</strong><br />
flowers/spike. Mahgoub et al (2006) studied the effect <strong>of</strong> the nitrogen levels 30, 40, 50 and 60 g/m 2 as<br />
ammonium nitrate (33.5 % N) and the level <strong>of</strong> 25, 30, 35 and 40 g/m 2 as potassium sulfate (48 % K2O).<br />
They found that Iris bulbs showed higher values for plant height, fresh and dry weight <strong>of</strong> leaves (40 g<br />
N + 30 g K /m 2 ) N level up to 60 g/m 2 showed stimulatory effect on chlorophyll a, b and carotenoids,<br />
60 g N/m 2 increased carbohydrate percentage in the presence <strong>of</strong> 30 g /m 2 K, (40 g N/m 2 + 25 g K /m 2 )<br />
recorded high values <strong>of</strong> N, P and K in Iris leaves.<br />
The aim <strong>of</strong> this work is to study the response <strong>of</strong> Schefflera arboricola plants to foliar fertilizer <strong>of</strong><br />
Grow-more and nitrogen fertilizer and their interactions on growth and some chemical composition.<br />
MATERIALS AND METHODS<br />
The experiments was conducted at Research and Production Station <strong>of</strong> National Research Centre at<br />
Nubaria during two successive seasons 2007 and 2008 to investigate the response <strong>of</strong> Schefflera<br />
arboricola plant to foliar fertilizer micro nutrients and nitrogen fertilizer (ammonium nitrate 33.5 %)<br />
on growth and some chemical composition. On the third week <strong>of</strong> February 2007 and 2008 seasons,<br />
vegetative uniform cutting (20-24 cm length) were taken from Schefflera arboricola plant, cutting<br />
were treated for a minute with 1000 mg/L indole butric acid before planting in pots to enhance rooting.<br />
Rooted cuttings were planted in black plastic pots (10 cm) in diameter (one plant /pot) and grown in<br />
shaded green house media formulated by combination <strong>of</strong> peatmoss and sandy soil (1:1, v/v). The<br />
seedling were transplanted on 20 th April 2007 and 2008 seasons, in plastic pot (30 cm) in diameter<br />
filled with 10 kg <strong>of</strong> peatmoss and sandy soil (1:1, v/v) arranged in a complete randomized design with<br />
three replicates. Each replicate consists <strong>of</strong> three plants. Water requirements were relative humidity<br />
maintained between 45-65%, allow the surface <strong>of</strong> potting media to dry slightly before irrigation. Each<br />
pot was fertilized twice with 1.5 g nitrogen as ammonium nitrate (33.5% N) and 1.0 g potassium<br />
sulphate (48.5 % K2O). The fertilizers were applied at 30 and 60 days after transplanting. Phosphorus<br />
as calcium superphosphate (15.5 % P2O5) was mixed with soil before transplanting at a rate <strong>of</strong> 3.0 g/<br />
pot. Other agricultural processes were performed according to normal practice. Plants were sprayed<br />
with different concentration <strong>of</strong> foliar fertilizer (Gropw-more) Table (1) which produced by Ajemco<br />
International company at the rate <strong>of</strong> (0.0, 1.0 and 2.0 cm 3 /L). Nitrogen as ammonium nitrate was<br />
fertilized with (0, 100 and 200 kg), interaction <strong>of</strong> the two factors had been also carried out, in addition<br />
to untreated plants (control) which were sprayed with tap water. Foliar application <strong>of</strong> Grow-more and<br />
nitrogen was carried out two times <strong>of</strong> 30 days intervals starting at 20 July at both seasons. The<br />
experiments were sat in completely Randomized Design (CRD) with three replicates and two factors.<br />
The following data were recorded on 1 st week <strong>of</strong> December 2007 and 2008 season, the recorded data<br />
were plant height (cm), stem diameter (mm), No. <strong>of</strong> leaves, leaf area (cm 2 ) <strong>of</strong> 4 and 5 base leaves, fresh<br />
and dry weight <strong>of</strong> plant organs (gm). Photosynthetic pigments i.e. chlorophyll (a, b and carotenoids)<br />
were determined exactly 0.1 gm <strong>of</strong> fresh leaves <strong>of</strong> schefflera plant using the Spectrophotometric<br />
method developments by Metzzner et al (1965). Total nitrogen was determined by Chapman and Pratt<br />
(1961), while phosphorus determination carried out Colorimtrically according to King (1951). Potassium<br />
was determined photometrically by flam photometer method as described by Brown and Lillan (1946).<br />
Data obtained were subjected to standard analysis <strong>of</strong> variance procedure, the values <strong>of</strong> LSD were<br />
obtained whenever F value were significantly as 5% levels reported by Snedecor and Cochran (1980).<br />
178
Growth characters:<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
RESULTS AND DISCUSSION<br />
Data in Table (2) show that foliar application <strong>of</strong> Grow-more at the concentration <strong>of</strong> 1.0 and 2.0 cm 3 /L<br />
on schefflera plants significantly increased all growth parameters plant height (cm), No. <strong>of</strong> leaves, fresh<br />
and dry weight <strong>of</strong> plant organs (gm), root and stem (gm), stem diameter and leaf area (cm 2 ) than the<br />
untreated plants, the highest values <strong>of</strong> previous characters were found when plants treated with 2.0<br />
cm3/L <strong>of</strong> grow-more followed by 1.0 cm 3 /L. These results are agreement with El-Fouly (2001) who<br />
noticed that the number <strong>of</strong> leaves and leaf area <strong>of</strong> sunflower plants were increased by addition <strong>of</strong> Fe,<br />
Mn, Zn, root size was increased by addition <strong>of</strong> Fe and Mn only. Rabie et al (2002) reported that foliar<br />
fertilizer containing N, P, K, Fe, Mn and Zn pronounced increases in dry weight, macro and<br />
micronutrients content <strong>of</strong> sorghum plants than control plants. Negm and Zahran (2001) found that,<br />
foliar application <strong>of</strong> micronutrients had the significant effect on increasing wheat grain and straw<br />
yields; yield attributes (plant height, spike length and 1000 grains weight). El -Quesni et al (2009)<br />
mentioned that using inorganic fertilizers at the concentrations <strong>of</strong> 1.0 and 2.0 cm 3 /L on syngonium<br />
plants increased plant height, stem diameter, No. <strong>of</strong> leaves/plant, leaf area and fresh and dry weight <strong>of</strong><br />
roots and leaves. These results may be due to micronutrient boron which helps transport vital sugars<br />
through plant membranes and promotes proper cell division, cell wall formation and development, also<br />
due to zinc which promotes seed/grain formation, plant maturity, acts as enzyme activator in protein,<br />
hormone (i.e. IAA) and RNA / DNA synthesis and metabolism. Chlorine also indirectly affects plant<br />
growth by stomatal regulation <strong>of</strong> water loss. Molybdenum has a significant effect on pollen formation,<br />
so fruit and grain formation are affected by molybdenum –deficient plants.<br />
With regard to the effect <strong>of</strong> nitrogen fertilizer on schefflera plants data in Table (2) illustrated that<br />
using nitrogen fertilizer at the rate <strong>of</strong> 100 kg gave significant increases than control plants. 200 kg<br />
nitrogen gave the highest values in all growth parameters under study compared with control plants.<br />
These results are in agreement with Ramesh et al (2002) they mentioned that plant height increased<br />
with increasing the rate <strong>of</strong> nitrogen. In this respect, Paradahan et al (2004) on gladiolus c.v. red<br />
mention that 4 g/m2 N plus K fertilizer at the rate <strong>of</strong> 30 g/m2 recorded highest value <strong>of</strong> number, fresh<br />
and dry weight <strong>of</strong> leaves as plant height . As regarding the interaction treatments, foliar application<br />
micronutrients and nitrogen fertilizer, the data show that significantly increased all growth characters<br />
under study. The highest values <strong>of</strong> growth characters were obtained by grow-more 2.0 cm 3 /L<br />
combined with ammonium nitrate at the rate <strong>of</strong> 200 kg /fed followed by grow-more 2.0 cm3/L and N at<br />
the rate <strong>of</strong> 200 kg/fed.<br />
Data emphasized the interaction effect were significantly affected all growth parameters i.e. plant<br />
height (cm), number <strong>of</strong> leaves, fresh and dry weight <strong>of</strong> (leaves, root and stem) stem diameter and leaf<br />
area <strong>of</strong> schefflera arboricola L. plants. These results may be due to increasing the nitrogen levels<br />
which delays senescence and stimulates growth and also changes plant morphology, particularly if the<br />
nitrogen availably is high in the rooting medium during the early growth (Levin et al, 1989; Olsthoorn<br />
et al 1991), it presumably related to nitrogen induced changes in the phytohormone balance (Sommer<br />
and Six 1982).<br />
Chemical constituents:<br />
Synthetic Pigments:<br />
Data in Table (3) indicated that spraying schefflera plants with grow-more at the rate <strong>of</strong> 1.0 cm3/L<br />
increasing significantly in chl. a, b and total chlorophyll and decreased in total carotenoids content<br />
whereas 2.0 cm3/L gave the highest values in the content <strong>of</strong> plants from Chl. a, Chl. b, total<br />
Chlorophyll and total carotenoids content. These results were agreement with those obtained by<br />
Ratanarat et al (1990), El-Quesni et al (2009) they found that the highest values <strong>of</strong> Chl. a, Chl. b and<br />
total carotenoids in syngonium plants increases by increasing the concentration <strong>of</strong> grow-more up to 2.0<br />
cm3/L. These results may be due to iron, manganese, which promote chlorophyll production and<br />
photosynthesis process, copper which helps in chlorophyll formation. With regard to the effect <strong>of</strong><br />
nitrogen fertilizer on schefflera plants data in Table (3) showed that the two used concentration <strong>of</strong> N<br />
fertilizer increasing Chl. a, b and total Chlorophyll whereas total carotenoids content gave significant<br />
increased by using 200 kg N only. These results are agreement with Mahgoub et al (2006) on Iris<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
bulbs they mentioned that maximizing the rate <strong>of</strong> N up to 60 g/m2 showed the stimulatory effect on<br />
chlorophyll a, b and carotenoids irrespective <strong>of</strong> the K fertilizer level.<br />
Concerning the effect <strong>of</strong> interaction on photosynthetic pigments data show that the highest significant<br />
values was found in plant treated with 2.0 cm2/L grow-more fertilizer plus 200 kg nitrogen fertilizer<br />
followed by 2.0 cm3/L micronutrients and 100 N , respectively. These treatments may be due to<br />
positive effect on growth parameters.<br />
Mineral Ions content:<br />
Data in Table (3) found that foliar application <strong>of</strong> grow-more at the concentration <strong>of</strong> 1.0 and 2.0 cm 3 /L<br />
and nitrogen fertilizer at the rate <strong>of</strong> 100 and 200 kg increased the total amount <strong>of</strong> nitrogen, phosphorus<br />
and potassium ions content on schefflera plants compared with control plants. These results were<br />
agreement with those obtained by Sharma et al (2002) they found that application <strong>of</strong> organic material<br />
either alone or in combination with chemical fertilizers caused substantial increase in total N, available<br />
P, K as well as increased wheat and straw yield Mahgoub et al(2006) on Iris bulbs they found that<br />
using 40 g/m2 N plus 25 g/m 2 K recorded high values <strong>of</strong> N, P and K in Iris leaves. With regard the<br />
effect <strong>of</strong> interaction in mineral ions content data show that significantly increased N, P and K content<br />
<strong>of</strong> schefflera plants were obtained by grow-more 2 cm 3 /L combined with 200 kg N followed by grow<br />
more 2 cm 3 /L.<br />
Data in Table (3) mentioned that total protein percentage increased by (6.46 and 10.53) when plants<br />
treated with 1.0 and 2.0 cm 2 /L grow-more respectively compared with control plants which recorded<br />
(8.68 %). Also nitrogen fertilizer 100 and 200 kg treatments in the total protein increased by (9.68 and<br />
10.09 %) respectively than control plants (8.90 %).<br />
The highest recorded data in total protein percentage were (11.21, 10.69 and 10.19) obtained from 2<br />
cm 3 /L micronutrients plus 200 kg nitrogen fertilizer followed by 2 cm 3 /L and 200 kg N respectively.<br />
These results are in line with those obtained by Negm and Zahran (2001) they mentioned that<br />
micronutrients increased protein grain content in wheat plants and El-Quesni et al (2009) on<br />
syngonium plants. These increments led to positive effect <strong>of</strong> growth parameters and enhancing effect<br />
on plant metabolism which was regarded as a better indicator for foliage plants.<br />
Table (1) Chemical properties <strong>of</strong> micronutrients fertilizer grow-more used in this study.<br />
Growmore<br />
content<br />
N2 P2O5 K2O Fe Zn Mg Ca Cu S B Mo<br />
% 11 6 8 0.15 0.15 0.14 0.02 0.20 0.02 0.01 0.01<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table (2) Effect <strong>of</strong> micronutrient and nitrogen fertilizer on vegetative growth <strong>of</strong> schefflera arboricola<br />
L. plants. (means <strong>of</strong> two seasons 2007 and 2008).<br />
Character<br />
Treatments<br />
Effect <strong>of</strong> micronutrient<br />
Plant<br />
height<br />
Stem<br />
diam<br />
eter<br />
Control 37.61 1.21<br />
Micro 1 cm 3 /L 33.84 1.24<br />
Micro 2 cm 3 /L 42.97 1.46<br />
No.o<br />
f<br />
leave<br />
s<br />
181<br />
Leaf<br />
area<br />
F.W<br />
<strong>of</strong><br />
root<br />
D.W<br />
<strong>of</strong><br />
root<br />
F.W<br />
<strong>of</strong><br />
leave<br />
s<br />
cm mm cm 2 gm<br />
18.6<br />
2<br />
19.9<br />
0<br />
22.2<br />
7<br />
8.87<br />
9.56<br />
11.6<br />
6<br />
39.6<br />
2<br />
41.4<br />
0<br />
45.0<br />
8<br />
17.5<br />
3<br />
36.6<br />
7<br />
41.3<br />
7<br />
75.6<br />
8<br />
76.9<br />
2<br />
84.6<br />
3<br />
D.W<br />
<strong>of</strong><br />
leave<br />
s<br />
26.6<br />
6<br />
26.9<br />
3<br />
29.8<br />
8<br />
F.W<br />
<strong>of</strong><br />
stem<br />
35.7<br />
6<br />
36.6<br />
7<br />
41.3<br />
7<br />
LSD at 5% level 1.41 0.07 1.58 1.54 1.41 2.09 3.69 1.88 2.09 1.48<br />
Effect <strong>of</strong> nitrogen<br />
Control 39.91 1.23<br />
N 100 kg 39.36 1.25<br />
N 200 kg 41.10 1.42<br />
19.8<br />
6<br />
19.5<br />
0<br />
21.4<br />
2<br />
9.10<br />
9.80<br />
11.1<br />
8<br />
41.2<br />
2<br />
41.7<br />
9<br />
43.0<br />
9<br />
18.0<br />
5<br />
19.2<br />
0<br />
20.3<br />
8<br />
77.0<br />
3<br />
78.0<br />
6<br />
82.1<br />
4<br />
26.2<br />
0<br />
27.0<br />
5<br />
29.2<br />
1<br />
30.9<br />
1<br />
37.4<br />
0<br />
39.5<br />
0<br />
LSD at 5% level 1.41 0.07 1.58 1.54 1.40 1.70 3.69 1.88 2.09 1.48<br />
Effect <strong>of</strong> interaction<br />
Control 32.00 1.11<br />
Micro 1 cm 3 /L 41.38 1.28<br />
Micro 2 cm 3 /L 43.34 1.32<br />
N 100 kg 40.17 1.26<br />
N 200 kg 40.67 1.27<br />
Micro 1 cm 3 /L + N<br />
100 kg<br />
Micro 1 cm 3 /L + N<br />
200 kg<br />
Micro 2 cm 3 /L + N<br />
100 kg<br />
Micro 2 cm 3 /L + N<br />
200 kg<br />
38.67 1.24<br />
36.42 1.20<br />
39.25 1.25<br />
46.33 1.80<br />
14.7<br />
3<br />
22.0<br />
2<br />
22.8<br />
3<br />
19.8<br />
3<br />
21.2<br />
8<br />
19.0<br />
0<br />
18.6<br />
6<br />
19.6<br />
7<br />
24.3<br />
2<br />
6.33<br />
10.2<br />
9<br />
10.6<br />
8<br />
10.0<br />
7<br />
10.2<br />
0<br />
9.39<br />
9.00<br />
9.95<br />
14.3<br />
4<br />
33.5<br />
4<br />
43.7<br />
4<br />
46.3<br />
8<br />
42.0<br />
0<br />
43.3<br />
3<br />
41.5<br />
5<br />
38.9<br />
0<br />
41.8<br />
3<br />
47.3<br />
0<br />
12.5<br />
7<br />
20.3<br />
1<br />
21.2<br />
7<br />
19.8<br />
5<br />
20.1<br />
7<br />
18.1<br />
5<br />
17.0<br />
7<br />
19.6<br />
0<br />
23.9<br />
0<br />
67.0<br />
7<br />
81.6<br />
8<br />
82.3<br />
3<br />
80.3<br />
0<br />
79.6<br />
7<br />
76.2<br />
5<br />
72.8<br />
3<br />
77.6<br />
3<br />
93.9<br />
3<br />
21.1<br />
2<br />
28.1<br />
7<br />
29.3<br />
3<br />
27.7<br />
8<br />
28.0<br />
7<br />
26.2<br />
1<br />
25.4<br />
2<br />
27.1<br />
7<br />
33.1<br />
5<br />
28.1<br />
3<br />
40.8<br />
7<br />
41.4<br />
2<br />
39.3<br />
3<br />
39.8<br />
0<br />
35.7<br />
8<br />
33.3<br />
7<br />
37.0<br />
9<br />
45.3<br />
2<br />
LSD at 5% level 2.44 0.11 2.73 2.66 2.44 2.94 6.39 3.01 3.61 2.56<br />
Micro= micronutrients, F.W.=fresh weight,D.W.=dry weight , N= nitrogen<br />
D.W<br />
<strong>of</strong><br />
stem<br />
15.0<br />
1<br />
16.8<br />
5<br />
21.1<br />
2<br />
16.4<br />
1<br />
16.7<br />
3<br />
19.8<br />
9<br />
11.0<br />
7<br />
18.0<br />
0<br />
20.1<br />
7<br />
16.9<br />
8<br />
17.0<br />
0<br />
16.5<br />
4<br />
11.0<br />
0<br />
16.6<br />
7<br />
26.5<br />
3
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Table (3) Effect <strong>of</strong> micronutrient and nitrogen fertilizer on chemical constituents <strong>of</strong> schefflera<br />
arboricola L. plants. (means <strong>of</strong> two seasons 2007 and 2008).<br />
Treatments<br />
Character<br />
Effect <strong>of</strong> micronutrient<br />
Chlorophylls Total<br />
Chl. a Chl. b<br />
Chl.<br />
a+b<br />
182<br />
caroten<br />
oids<br />
Mineral ions contents<br />
N P K<br />
mg/g %<br />
Total<br />
protein<br />
Control 0.99 0.30 1.29 0.17 1.47 0.25 3.23 8.68<br />
Micro 1 cm 3 /L 1.12 0.33 1.45 0.18 1.52 0.27 3.26 9.46<br />
Micro 2 cm 3 /L 1.29 0.41 1.70 0.25 1.62 0.33 4.12 10.53<br />
LSD at 5% level 0.08 0.08 0.09 0.09 0.03 0.02 0.33 0.39<br />
Effect <strong>of</strong> nitrogen<br />
Control 1.03 0.33 1.36 0.19 1.51 0.27 3.32 8.90<br />
N 100 kg 1.18 0.34 1.50 0.19 1.52 0.27 3.42 9.68<br />
N 200 kg 1.19 0.38 1.57 0.22 1.59 0.30 3.87 10.09<br />
LSD at 5% level 0.08 0.02 0.09 0.02 0.03 0.02 0.33 0.39<br />
Effect <strong>of</strong> interaction<br />
Control 0.52 0.17 0.69 0.09 1.19 0.15 2.50 5.83<br />
Micro 1 cm 3 /L 1.26 0.40 1.66 0.23 1.63 0.32 3.46 10.17<br />
Micro 2 cm 3 /L 1.31 0.43 1.75 0.26 1.67 0.35 4.00 10.69<br />
N 100 kg 1.22 0.36 1.58 0.21 1.60 0.28 3.63 10.00<br />
N 200 kg 1.24 0.37 1.61 0.22 1.65 0.30 3.55 10.19<br />
Micro 1 cm 3 /L + N 100 kg 1.13 0.31 1.44 0.17 1.47 0.25 3.23<br />
Micro 1 cm 3 /L + N 200 kg 0.96 0.29 1.25 0.13 1.43<br />
9.35<br />
0.22 3.10 8.80<br />
Micro 2 cm 3 /L + N 100 kg 1.18 0.37 1.50 0.18 1.48 0.26 3.39 9.69<br />
Micro 2 cm 3 /L + N 200 kg 1.37 0.47 1.83 0.30 1.70 0.39 4.96 11.21<br />
LSD at 5% level 0.15 0.04 0.15 0.03 0.06 0.04 0.56 0.67<br />
Micro= micronutrients, Chl. Chlorophyll, N= nitrogen
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
REFERENCES<br />
Brady Nyle C. and R. Weil Ray. (2000). Elements <strong>of</strong> The Nature and Properties <strong>of</strong> Soil. Upper saddle<br />
Rover, New Jersy: Prentice-Hill Inc<br />
Brown, J.D. and O. Lilliland, (1946). Rapid determination <strong>of</strong> potassium and sodium in plant material<br />
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Chapman, H.D. and P.F. Pratt (1961). Methods <strong>of</strong> Analysis for Soil, Plants and Waters. Univ.<br />
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Dahiya, S.S., S.. Mohansundram, Sukhbi-Singh, S. Dahiya- Dsgnd Singh (2001). Effect <strong>of</strong> nitrogen<br />
and phosphorus on growth and dry matter yield <strong>of</strong> tuberose (Polianthus tuberose L.).<br />
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El-Fouly, M.M.; O.A. N<strong>of</strong>al and Z.M. Mobarak (2001). Effects <strong>of</strong> soil treatment with iron, manganese<br />
and zinc on growth and micronutrient uptake <strong>of</strong> sunflower plants grown in high-pH soil.<br />
<strong>Journal</strong> <strong>of</strong> Agronomy and Crop <strong>Science</strong>. 186(4): 245-251.<br />
King, E.J. (1951). Microanalysis in Medical Biochemistry, 4 th E dn. J. and Ehar Chill. Ltd., London.<br />
Kohnk, Helmut and D. Franzmier, (1995). Soil <strong>Science</strong> Simplified. USA: Waveland Press Inc.<br />
Levin, S.A., H.A. Mooney and C. Field (1989). The dependence <strong>of</strong> plant root: shoot ratios on internal<br />
nitrogen concentration. Ann. Bot. (London)64, 71-75.<br />
Mahgoub, H.M.; Rawia, A. Eid, and Bedour, H. Abou Leila (2006). Response <strong>of</strong> Iris bulbs growth in<br />
sandy soil to nitrogen and potassium fertilization. <strong>Journal</strong> <strong>of</strong> applied <strong>Science</strong>s Research, 2(11):<br />
899-903.<br />
Massoud, A.M.; M.Y. Abou Zaid and M.A. Bakry (2005). Response <strong>of</strong> pea plants grown in silty clay<br />
soil to micronutrients and Rhizobium incubation. Egypt.J.Appl. Sci., 20: 329-346.<br />
Metzzner, H., H. Rava and H. Senger (1965). Unter suchungen zur synchronis iebekiety pigments<br />
mangel von chlrella. Planta, 65: 186-190.<br />
Negm, A.Y. and F.A. Zahran (2001). Optimization time <strong>of</strong> micronutrient application to wheat plants<br />
grown on sandy soils. Egyptian <strong>Journal</strong> <strong>of</strong> Agricultural Research 79(3): 813-823.<br />
Ol sthoorn,A.F.M.; W.G.Keltjens,B.Van Braen and M.C.G.Hopman (1991).Infleunce <strong>of</strong> ammonium on<br />
fine root development and rhizosphere PH <strong>of</strong> douglas seedlings in sand plant soil 133:75-<br />
81.<br />
Pal, A.K. and B.Biswas (2005). Response <strong>of</strong> fertilizer on growth and yield <strong>of</strong> tuberose (Poliathus<br />
tuberose L.) c.v. Calcutta single in the plains <strong>of</strong> west Bengal. J. Interacadimica, Nadia, India,<br />
9: 1, 33-<br />
Paradhan, A.; J.N. Mishra and P.C. Lenka (2004). Effect <strong>of</strong> N and K growth and yield <strong>of</strong> gladiolus.<br />
Orissa <strong>Journal</strong> <strong>of</strong> Horticulture. Orissa Horticultural Society, Bhubaneswar, India. 32: 74-77.<br />
Rabie, M.H.; I.A. Ibrahim, I. A. Attia and E.A. Zahran (2002). Effect <strong>of</strong> enriched starch phosphate and<br />
carbamate as natural foliar fertilizers on yield and mineral content <strong>of</strong> sorghum. Egyptian<br />
<strong>Journal</strong> <strong>of</strong> Agricultural Research . 80(3): 971-984.<br />
Ramesh Kumar, Sheo Ghind and D.S.Yadov (2002). <strong>Studies</strong> on N and P requirement <strong>of</strong> tuberose<br />
(Polianthus tuberosa Linn) c.v. single in hilly soils. Haryana <strong>Journal</strong> <strong>of</strong> Horticultural <strong>Science</strong>,<br />
Haryana Society <strong>of</strong> Haryana, H::Sar, India, 31:1/2, 52-54.<br />
Ratanarat, S.; W. Masangsan; P. Vacleesirisak; C. Distsantia and V. Phanuvas (1990). Effects <strong>of</strong> ion<br />
foliar spray and specific Rhizobium strains on yield components <strong>of</strong> three peanut cultivars. In:<br />
Proceedings 8 th National Ground.nut Research.Meeting.3-5May 1989,Roi-Et,Thiland.<br />
Sharma, S.R; S.C.Bh Andari; H.S. Purohit (2002). Effect <strong>of</strong> organic manure and mineral nutrients<br />
on nutrient uptake and yield <strong>of</strong> cowpea. <strong>Journal</strong> <strong>of</strong> Indian Society <strong>of</strong> Soil <strong>Science</strong>. 50(4): 475-<br />
480.<br />
183
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
Smirn<strong>of</strong>f ,N and G.R. Stewart (1985). Nitrate assimilation ion and translocation by higher plants.<br />
Comparative physiology and ecological consequences. Physiol. Plant 64:133-140.<br />
Snedecor, G.W. and W.G. Cochran.1980 Statistical Method 7 th Ed<br />
.IowstateUniv.Press,Iowa,USA.<br />
Sommer, K.andR.six(1982).Ammonium als stickst<strong>of</strong>f qelle beim anbau von<br />
Fttergerste.Landw.Forsch.38:151-161.<br />
Uph<strong>of</strong>, J.C. Th. (1959). Dictionary <strong>of</strong> Economic plants, Weinheim. An excellent and very<br />
comprehensive guide but it only gives very short descriptions <strong>of</strong> the uses without any details<br />
<strong>of</strong> how to utilize the plants.<br />
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<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
ISSN 1943-2429<br />
© 2010 <strong>Ozean</strong> Publication<br />
STATISTICAL MODELLING FOR OUTLIER FACTORS<br />
Ahmet Kaya<br />
Ege University, Tire Kutsan Vocational High School Computer Programming Department,<br />
Tire-İzmir, Turkey.<br />
e-mail address for correspondence: ahmet.kaya@ege.edu.tr<br />
____________________________________________________________________________________<br />
Abstract. Error in data is one <strong>of</strong> the facts that cause the parameter estimations to be subjective. If the<br />
erroneous case is proved statistically, then these cases are called outliers. Outliers are defined as the few<br />
observations or records which appear to be inconsistent with the rest <strong>of</strong> the group <strong>of</strong> the sample and more<br />
effective on prediction values. Isolated outliers may also have positive impact on the results <strong>of</strong> data<br />
analysis, data mining and estimated model. In this study, we are concerned with outliers in time series<br />
which have two special cases, innovational outlier (IO) and additive outlier (AO). The occurence <strong>of</strong> AO<br />
indicates that action is required, possibly to adjust the measuring instrument or mistake made by person<br />
in observation or record. However, if IO occurs, no adjustment <strong>of</strong> the measurement operation is required.<br />
Also in the study, a multi-factor ( 3 42<br />
2<br />
) modelling was done in order to fit the effects <strong>of</strong> model in data<br />
analysis AR(1) coefficients, (0.5, 0.7, 0.9) outlier type (AO, IO), serie wideness (50, 100, 200, 500) and<br />
criterion value sensibility (% 99 (C=3.00), % 95 (C=3.50), % 90 (C=4.00)) factors statistically by<br />
making use <strong>of</strong> a simulation study. The results <strong>of</strong> the variance analysis on outlier factors were also<br />
emphasized.<br />
Key Words: ARMA, Outliers in Time Series, AO, IO, Modelling outlier factors.<br />
___________________________________________________________________________________<br />
INTRODUCTION<br />
Real data and databases may <strong>of</strong>ten include some erroneous parts. These situations, which damage the<br />
characteristics <strong>of</strong> data are called “abnormal condition”, and the values, which cause these “abnormal<br />
condition” are called outliers. The outliers, which are really independent, are the situations that cause the<br />
parameter estimation values in modelling to be subjective, they damage the processes even though they<br />
are set properly, and it is an obligation to destroy or to eliminate the effects. They diminish the reliability<br />
<strong>of</strong> the results. In this case, outliers is the name given to the data or data sets, which are inharmonious with<br />
the rest <strong>of</strong> the serie, cause the parameter estimation values to be subjective, and damage the settled<br />
processes.<br />
The outliers are values which seem either too large or too small as compared to rest <strong>of</strong> the observations<br />
(Gumbel, 1960).<br />
An outlying observation, or outlier, is one that appears to deviate markedly from other members <strong>of</strong> the<br />
sample in which it occurs (Grubbs, 1969).<br />
The detection <strong>of</strong> influential subsets or multiple outliers is more difficult, owing to masking and swamping<br />
problems. Masking occurs when one outlier is not detected because <strong>of</strong> the presence <strong>of</strong> others, while<br />
swamping occurs when a non-outlier is wrongly identified owing to the effect <strong>of</strong> some hidden outliers<br />
(Pena and Yohai, 1995).<br />
Data analysis is done by adapting the data to a time series model which is composed <strong>of</strong> observations.<br />
Outliers in time series were first studied by Fox in 1972. Fox has developed a criterion to fix the outliers<br />
which is called likelihood ratio criteria, and defined the outliers as the first and second type outliers. The<br />
simulations made have proved that the most effective method among these is the consecutive method,<br />
185
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
developed by Chang(1982), Chang and Tiao(1983). Hillmer(1983) Tsay(1986), Pena(1987), Abraham<br />
and Yatawara(1988), Bruce and Martin(1989) had some studies which contributed the theorical structure<br />
<strong>of</strong> the consecutive method. Besides, Abraham and Yatawara(1988) have studied on lagrange multiplier<br />
method or score based outlier tests. Pena(1987), Abraham and Chuang(1989) and Bruce and<br />
Martin(1989) have studied about the tests depending on the elimination <strong>of</strong> the outlier values during<br />
outlier detection and effective observations in time series (Ljung, 1993).<br />
Isolating Outliers<br />
The main reason for isolating outliers is associated with data quality assurance. The main exceptional<br />
values are more likely to be incorrect. According to the definition given by Wand and Wang (1996),<br />
unreliable data represents an unconformity between the state <strong>of</strong> the database and the state <strong>of</strong> the real<br />
world. For a variety <strong>of</strong> database applications, the amount <strong>of</strong> erroneous data may reach to ten percent and<br />
even more.<br />
It is well known that outliers can seriously affect any inferences drawn if they are not treated<br />
appropriately. Their detection and treatment, however, can lead to considerably greater computational<br />
process. For that reason, removal <strong>of</strong> outliers effect can improve the quality <strong>of</strong> data used for statistical<br />
inferences. Isolated outliers may also have positive impact on the results <strong>of</strong> data analysis and data mining.<br />
Simple statistical estimates, like sample mean and standard deviation can be significantly biased by<br />
individual outliers that are far away from the middle <strong>of</strong> the distribution.<br />
Outlier Detection<br />
The purpose <strong>of</strong> outlier detection is to discover the unusual data, whose behavior is very exceptional when<br />
compared to the rest <strong>of</strong> the data set. Examining the extraordinary behavior <strong>of</strong> outliers helps to uncover the<br />
valuable knowledge hidden behind them and to help the decision makers to make pr<strong>of</strong>it or improve the<br />
service quality. Hence, mining aiming to detect outlier is an important data mining research with<br />
numerous applications, which include credit card fraud detection, discovery <strong>of</strong> criminal activites in<br />
electronic commerce, weather prediction, marketing, statistical applications and so on.<br />
Detection methods are divided into two parts: univariate and multivariate methods. In univariate methods,<br />
observations are examined individually and in multivariate methods, associations between variables in<br />
the same dataset are taken into account.<br />
Classical outlier detection methods are powerful when the data contain only one outlier. However, these<br />
methods decrease drastically if more than one outliers are present in the data (Hadi, 1992).<br />
Although manual inspection <strong>of</strong> scatter plots is the most common approach to outlier detection, this is not<br />
the most effective method. Since the multidimensionality <strong>of</strong> databases provides a significant advantage to<br />
automated perceptions <strong>of</strong> outliers over the manual analysis <strong>of</strong> visualized data. Unlike the case <strong>of</strong> human<br />
decision-making, the parameters <strong>of</strong> the automated detection <strong>of</strong> outliers can be completely controlled,<br />
making it an objective tool for data analysis. Outlier detection in a database is to enhance the performance<br />
<strong>of</strong> data mining algorithms (Last and Kendal, 1995).<br />
Before we address the issue <strong>of</strong> identifying these outliers, we must emphasize that not all are wrong<br />
numbers. They may justifiably be part <strong>of</strong> the group and may lead to better understanding <strong>of</strong> the<br />
phenomena being studied. When an outlier is detected, the analyst is faced with number <strong>of</strong> questions<br />
(David,1978) :<br />
� Is the measurement process out <strong>of</strong> control?<br />
� Is the model wrong?<br />
� Is some transformation required?<br />
� Is there an identifiable subset <strong>of</strong> observations that is important in its different behavior?<br />
OUTLIER MODEL<br />
A mathematical definition <strong>of</strong> a stationary time series is that a time series is said to be stationary if there is<br />
no systematic change in mean (no trend) if there is no systematic change in variance, and if strictly<br />
periodic variations have been removed (Chatfield, 1991).<br />
Now, Consider a stationary autoregressive moving average (ARMA) process <strong>of</strong> order ( p<br />
, q)<br />
186
t<br />
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
�( B ) z � �(<br />
B)<br />
e<br />
(1)<br />
�(<br />
B)<br />
� 1�<br />
� B � ... ��<br />
B<br />
1<br />
q<br />
� ( B)<br />
� 1�<br />
� B � ... ��<br />
B ,<br />
1<br />
t<br />
p<br />
q<br />
p<br />
,<br />
B<br />
e t is a sequence <strong>of</strong> independent and identically distributed random variables with mean zero and<br />
variance<br />
2<br />
� .<br />
Model (2) can also be written as<br />
t<br />
t<br />
k<br />
187<br />
z<br />
t<br />
� z<br />
t�k<br />
� ( B) z � e<br />
(3)<br />
2<br />
where � ( B) � �(<br />
B)<br />
/ �(<br />
B)<br />
�1<br />
��<br />
B ��<br />
B �...<br />
.<br />
1<br />
When estimating the impact <strong>of</strong> an AO (4) and <strong>of</strong> an IO (5), respectively, in a hypothetical situation in<br />
which all <strong>of</strong> time series parameters are known. Two types <strong>of</strong> outliers in time series introduced by Fox<br />
(1972), are additive and innovational.<br />
The additive outlier-AO model:<br />
It is the type <strong>of</strong> outliers that affects a single observation and occurs as a result <strong>of</strong> a mistake made by<br />
person in observation or record. This model, defined as “total outlier” in the literature, is shown as<br />
follows:<br />
y z � �x<br />
t<br />
t<br />
t<br />
2<br />
� (4)<br />
where y t is the observed value, � is the magnitude <strong>of</strong> outlier and<br />
Innovational outlier-IO model:<br />
x t<br />
�1 t � T �<br />
� �<br />
�<br />
�0<br />
Otherwise�<br />
It is the type <strong>of</strong> outliers that affects the subsequent observations starting from its position, in other words<br />
that occurs as a result <strong>of</strong> natural randomness. The model, defined as “randomness outlier” in the literature,<br />
is shown as follows:<br />
� ( B)<br />
yt ( et<br />
� �xt<br />
)<br />
�(<br />
B)<br />
� (5)<br />
Thus the AO case may be called a gross error model, since only the level <strong>of</strong> the T’th observation is<br />
affected. On the other hand, an IO represents an extraordinary shock at time point T influencing<br />
z T , zT<br />
�1,...<br />
through the dynamic system described by �( B) � �(<br />
B)<br />
/ �(<br />
B)<br />
(Chang, Tiao and Chen,<br />
1988).<br />
The occurence <strong>of</strong> AO indicates that action is required, possibly to adjust the measuring instrument or at<br />
least to print an error massage on the database. However, if IO occurs no adjustment <strong>of</strong> the measurement<br />
operation is required (Muirhead, 1986).<br />
The existence <strong>of</strong> AO can seriously bias the estimates <strong>of</strong> the ARMA coefficients and variance, whereas IO<br />
in general has much smaller effect (Chang Tiao and Chen, 1983).<br />
Most <strong>of</strong>ten only AO’s are troublesome, whereas IO’s <strong>of</strong>ten have very little effect. This is understandable,<br />
since an IO can be seen as an extreme disturbance, but an AO is always an observation separate from the<br />
rest <strong>of</strong> data. For example think <strong>of</strong> the residual <strong>of</strong> an AR(1) model. An IO only affects residual, at the date<br />
(2)
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<strong>of</strong> outlier. An AO, on the other hand, affects the next residual as well, thus inflating two consecutive<br />
residuals. This effect has several consequences for any further analysis <strong>of</strong> the residuals.<br />
According to some researchers, if there exist an AO type outlier in an observation set, its effects must be<br />
removed, however, in case an IO type outlier exists, it is accepted as it occured as a result <strong>of</strong> natural<br />
randomness and its effects must not be removed. Since natural randomness is a situation, which already<br />
exists in all phases <strong>of</strong> life, the notion <strong>of</strong> “these effects must be tolerated” is the valid thought.<br />
Distinguishing an AO From an IO:<br />
There is usually little information available in practice about what type the possible outlier might be<br />
possible might be AO or IO is more appropriate for a given situation. When a test <strong>of</strong> an inappropriate type<br />
is used, the detecting power the test could be substantially reduced. Furthermore, even if it is known that<br />
an outlier has occurred at a particular point, the possibly adverse effect <strong>of</strong> the outlier may not be easy to<br />
remove unless its nature is properly identified (Chang Tiao and Chen, 1988).<br />
Outliers’ Characteristics:<br />
In order to show the characteristics <strong>of</strong> and AO model, the data are “uncontrolled” concentration readings<br />
<strong>of</strong> a chemical process recorded at every two-hour interval, titled “Box-Jenkins A Series” was used. (See,<br />
Box-Jenkins, 1976).<br />
In case <strong>of</strong> AO, only the level <strong>of</strong> the T’th observation is affected. (See the table-1, and the graph-1)<br />
Moreover IO represents an extraordinary shock at time point T influcing z T , zT<br />
�1,...<br />
through the<br />
dynamic system described by �( B) � �(<br />
B)<br />
/ �(<br />
B)<br />
. (See the table-2, and chart-2).<br />
AO Description:<br />
Table 1, Box-Jenkins A Series observations from 38 to 48.<br />
1 2 3 4 5 AO 5 4 3 2 1<br />
38 39 40 41 42 43 44 45 46 47 48<br />
17.7 17.4 17.8 17.6 17.5 16.5 17.8 17.3 17.3 17.1 17.4<br />
When Table-1 observations which is shown above have been investigated, it can be seen that finding<br />
additive outlier don’t change the tendency <strong>of</strong> observations. Observations taken before T (occurence <strong>of</strong><br />
outlier) time same tendency as observations taken after. Thus, we conclude that this outlier is AO,<br />
because only level <strong>of</strong> the T’th observation is affected. This conclusion can be seen from the chart-1which<br />
is shown below.<br />
Chart 1, Box-Jenkins A series observations from 38 to 48<br />
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IO Description:<br />
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Table 2, Box-Jenkins A series observations from 59 to 69.<br />
1 2 3 4 5 IO 5 4 3 2 1<br />
59 60 61 62 63 64 65 66 67 68 69<br />
17.2 16.6 17.1 16.9 16.6 18.0 17.2 17.3 17.0 16.9 17.3<br />
When Table-2 observations which is shown above have been investigated, it can be seen that finding<br />
innovational outlier changes the tendency <strong>of</strong> observations. Observations taken from before T time<br />
different from after, it can be seen that observations value has been changed. Thus, we conclude that this<br />
outlier is IO, because at time point T influcing consecutive observations. z T , zT<br />
�1,...<br />
. This conclusion<br />
can be seen from the chart-2 which is shown below.<br />
Outlier Detection Algorithm:<br />
Chart 2, Box-Jenkins A Series observation from 59 to 69<br />
� Read observations from defined file.<br />
� Read estimated ARMA parameters, using statistical package programs.<br />
� Read calculated � j ’s from the estimated model.<br />
� Read ê t ’s to use<br />
2<br />
ˆ � a and find outliers.<br />
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� Read critical values C which can be 3.00, 3.50 and 4.00.<br />
� Do<br />
1.<br />
2<br />
Calculate the ˆ � a from the ê t ’s.<br />
2. Increase the index <strong>of</strong> the current value by one<br />
3. Calculate � 1.<br />
T , � 2.<br />
T .<br />
4. If � C then display T, IO.<br />
1.<br />
T �<br />
2.<br />
T �<br />
5. If � C then display T, AO.<br />
otherwise no outlier&stop<br />
6. Calculate effect <strong>of</strong> IO or AO and update on new value in file.<br />
7. Reallocate new ê T ’s<br />
� End Do.<br />
� Go Reading new observations from updated file and perform algoritm again.<br />
SIMULATION PROCESS<br />
A computer simulation is an attempt to model a real-life or hypothetical situation on a computer so that it<br />
can be studied to see how the system works. By changing variables, predictions may be made about the<br />
behaviour <strong>of</strong> the system Computer simulation has become a useful part <strong>of</strong> modelling many natural<br />
systems in physics, chemistry and biology, and human systems in economics and social sciences as well<br />
as in engineering to gain insight into the operation <strong>of</strong> those systems. Traditionally, the formal modeling <strong>of</strong><br />
systems has been via a mathematical model, which attempts to find analytical solutions enabling the<br />
prediction <strong>of</strong> the behaviour <strong>of</strong> the system from a set <strong>of</strong> parameters and initial conditions. Computer<br />
simulation is <strong>of</strong>ten used as an adjunct to, or substitution for, modeling systems for which simple closed<br />
form analytic solutions are not possible. There are many different types <strong>of</strong> computer simulation, the<br />
common feature they all share is the attempt to generate a sample <strong>of</strong> representative scenarios for a model<br />
in which a complete enumeration <strong>of</strong> all possible states would be prohibitive or impossible<br />
(http://en.wikipedia.org/wiki/Simulation# Computer_simulation)<br />
In this study I conducted a simulation study to obtain some inferences about the different AR(1)<br />
coefficients, series size, outlier types, and sensitivity coefficients. Table 1 shows the probability <strong>of</strong><br />
finding Additive Outlier-AO, and Innovational Outlier-IO, based on 10000 realizations <strong>of</strong> the AR(1) with<br />
� � 0.<br />
5,<br />
0.<br />
7,<br />
0.<br />
9 and the critical values are C � 3. 00,<br />
C � 3.<br />
50,<br />
C � 4.<br />
00 , For sizes<br />
n � 50,<br />
100,<br />
200,<br />
500 . The fact that critical value C � 3.<br />
00 is close to the 1%, C � 3.<br />
50 to the<br />
5% and C � 4.<br />
00 to the 10% significance level. The location <strong>of</strong> outliers is set in the middle <strong>of</strong> the<br />
observational period, spesifically T � 26 when n � 50 , T � 51 when n �100<br />
, T � 101 when<br />
n � 200 , and T � 251 when n � 500 (Kaya, 2004).<br />
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Table 3. Finding AO and IO probability<br />
based on 10000 replications <strong>of</strong> an AR(1) process.<br />
� n<br />
C=3.0<br />
AO IO<br />
C=3.5<br />
AO IO<br />
C=4.0<br />
AO IO<br />
50 0.34 0.38 0.33 0.37 0.322 0.35<br />
1 2 4 0 4<br />
100 0.44 0.48 0.42 0.46 0.431 0.46<br />
2 2 8 6 4<br />
0.5 200 0.57 0.61 0.55 0.59 0.540 0.57<br />
7 0 9 6 9<br />
500 0.62 0.66 0.61 0.65 0.609 0.64<br />
2 2 4 0 1<br />
50 0.52 0.56 0.52 0.55 0.512 0.55<br />
9 2 5 5 1<br />
100 0.62 0.66 0.61 0.65 0.607 0.64<br />
2 0 9 3 3<br />
0.7 200 0.65 0.68 0.63 0.66 0.622 0.65<br />
1 8 9 8 6<br />
500 0.75 0.78 0.74 0.77 0.723 0.75<br />
0 7 3 6 7<br />
50 0.64 0.67 0.63 0.67 0.621 0.66<br />
2 6 8 2 1<br />
100 0.69 0.72 0.68 0.72 0.681 0.71<br />
1 8 8 1 5<br />
0.9 200 0.79 0.83 0.79 0.83 0.782 0.81<br />
5 6 1 0 5<br />
500 0.90 0.94 0.89 0.93 0.875 0.90<br />
1 5 2 2 7<br />
STATISTICAL ANALYSIS<br />
Statistics is an increasingly important subject which is useful in many types <strong>of</strong> scientific investigation. It<br />
has become the science <strong>of</strong> collecting, analysing and interpreting data in the best possible way. Statistics is<br />
particularly useful in situations where there is experimental uncertainty and is <strong>of</strong>ten defined as the science<br />
<strong>of</strong> making decisions in the face <strong>of</strong> uncertainty. We begin with some scientific examples in which<br />
experimental uncertainty is present. Most formal statistical models used in different area have been<br />
linear, based on the principles <strong>of</strong> statistical inference, analysis <strong>of</strong> variance, regression and other models.<br />
Formal models may be a variety <strong>of</strong> different forms described by equation models and implemented using<br />
some special programming language which are Pascal, C, C+, C++, and also other special languages,<br />
such as LISP and PROLOG (Kaya and İkiz,2001).<br />
Models can be used for member <strong>of</strong> different purpose in research and management <strong>of</strong> production systems.<br />
Some uses are (Bywater and Cacho, 1994);<br />
� Classification <strong>of</strong> existing data<br />
� Identification <strong>of</strong> type <strong>of</strong> data in research<br />
� Taking results <strong>of</strong> experiments<br />
� Constructing and testing hypothesis<br />
� Estimating parameters<br />
� Concluding experimental results<br />
� Designing experimental production systems<br />
� Determining best production systems<br />
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MODELLING<br />
By using the simulation results a variance analysis study was made for putting forward how the factors<br />
like Model AR(1) Coefficients (M), (0.5, 0.7, 0.9), Series Size (W), (50, 100, 200, 500), Critical value<br />
sensitiveness (C), (C=3.00, C=3.50, C=4.00), Outlier Type (T) (AO, IO) are effective statistically in<br />
detecting outliers. The factors to solve such problems are;<br />
Model AR(1) coefficient (M)<br />
Series sizes (W)<br />
Critical value sensitiveness (C)<br />
Outlier type (T)<br />
The factor levels were selected properly and the model equation for multi-factored 3 42<br />
2<br />
experiment<br />
layout was designed as given below:<br />
Y � � M �W<br />
� C �T<br />
� �<br />
ijkl<br />
� (6)<br />
i<br />
i �1, 2,<br />
3;<br />
j �1,<br />
2,<br />
3,<br />
4;<br />
k �1,<br />
2,<br />
3;<br />
l �1,<br />
2<br />
j<br />
k<br />
l<br />
ijkl<br />
In this model Y ijkl represents the probability <strong>of</strong> outlier detection, � represents general average, i M<br />
represents AR(1) coefficients, j W represents the series sizes, C k represents critical value sensitiveness,<br />
T l represents outlier type, and � ijkl represents the error term.<br />
Table 4. Analysis <strong>of</strong> variance for Table 1.<br />
SOURCE DF Sum<br />
<strong>of</strong><br />
Square<br />
s<br />
AR(1) 2 0.8443<br />
1<br />
Series Size 3 0.6340<br />
9<br />
Critical 2 0.0054<br />
Value<br />
9<br />
Outlier 1 0.0231<br />
Type<br />
1<br />
Error 63 0.0324<br />
6<br />
Total 71 1.5394<br />
8<br />
192<br />
Mean<br />
Square<br />
0.4221<br />
6<br />
0.2113<br />
6<br />
0.0027<br />
5<br />
0.0231<br />
1<br />
0.0005<br />
2<br />
F P<br />
819. 0.000<br />
86<br />
410. 0.000<br />
20<br />
5.33 0.007<br />
44.8<br />
5<br />
CONCLUDING REMARKS<br />
0.000<br />
From the results <strong>of</strong> this experiment, some main important conclusions were emerged:<br />
� The data used in this study were obtained from the simulation experiments performed.<br />
Simulation results were reorganized and remodeled under a suitable experimental design. The<br />
type <strong>of</strong> factorial design was ( 3 4 2)<br />
2<br />
that is 2 factors each at 3 levels and two factors at 1 level<br />
each. Different AR(1) (0.5, 0.7, 0.9), sensitivity coefficients (3.00, 3.50, 4.00), series size n (50,<br />
100, 200, 500), outlier types (AO-IO) and were statistically significant.<br />
� AR(1) coefficients are the values that show the strength <strong>of</strong> the dependence among the<br />
observations. Therefore, it is easier to make outlier analysis on dependent observation sets. In<br />
other words, outlier detection is easier in series having more dependency among the<br />
observations.
<strong>Ozean</strong> <strong>Journal</strong> <strong>of</strong> <strong>Applied</strong> <strong>Science</strong>s 3(1), 2010<br />
� AO, known as the outlier value that occurs because <strong>of</strong> the user is detected more difficultly than<br />
IO, the outlier value that occurs as a result <strong>of</strong> natural randomness. The presence <strong>of</strong> AO in data<br />
causes loss <strong>of</strong> autocorrelation in outlier position. For that reason, finding IO is easier than<br />
finding AO.<br />
� For the sample lengths <strong>of</strong> n =50, 100, 200 and 500, the probability <strong>of</strong> detecting error is<br />
considered important. So data analysis being easier for large data is detained as a result.<br />
� Since the critical value sensitiveness is found as important and it is a factor showing the<br />
tolerance bounderies <strong>of</strong> the outlier analysis in outlier detection phase, it must be emphasized<br />
carefully.<br />
� The proposed procedure is demonstrated to be useful for estimating time series parameters when<br />
there is the possibility <strong>of</strong> outliers. It can be applied to all invertible models. Moreover, it is<br />
flexible and easy to interpret, and it can be implemented with very few modifications to existing<br />
s<strong>of</strong>tware packages capable <strong>of</strong> dealing with ARMA and transfer function models. In practice, we<br />
suggest that this procedure can be used in conjuction with other diagnostic tools for time series<br />
analysis to produce even better results (Chang, Tiao and Chen, 1988).<br />
Suggestions and Inferences:<br />
1. Before making the statistical tests on an observation set, outlier analysis must be done. By this way,<br />
test statistics can produce more healthy results.<br />
2. There are two types <strong>of</strong> outliers, possible to encounter. The effect <strong>of</strong> first type <strong>of</strong> outliers, which are<br />
caused by people, equipments and machines, must be eliminated. Since the second type <strong>of</strong> outliers<br />
occurs because <strong>of</strong> the natural randomness, the elimination <strong>of</strong> the effects <strong>of</strong> them is optional.<br />
3. The model, which is appropriate for the observation values must be used. If an inappropriate model is<br />
applied, the values which are not outliers may be considered as outliers.<br />
4. Outlier detection processes in time series are mutually attached with the autocorrelation powers <strong>of</strong><br />
the observations. For the observation sets, whose autocorrelation is low, the effect “hiding”, in which<br />
the outlier is not considered as an outlier, and the effect “dragging”, in which a non-outlier<br />
observation is considered as an outlier can be obtained.<br />
5. Since outlier detection processes are also used in quality control processes, which are concerned with<br />
finding error, their importance is increasing everyday.<br />
6. While detecting an outlier, the following components <strong>of</strong> the process are determined as important:<br />
a. Generosity <strong>of</strong> the error,<br />
b. Series size,<br />
c. Strong autocorrelation,<br />
d. Criterion value sensitiveness.<br />
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194