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ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
46
Diverse Distribution Study Of C-14 Through Out The Major Crops Of Punjab
(Pakistan) Using Biological Oxidizer And Liquid Scintillation Counter
MUHAMMAD ATTIQUE KHAN SHAHID1*
, IJAZ AHMAD KHAN1
, SAEED AHMAD1
,
MUHAMMAD RAFIQUE AASI2
, TAQMEEM HUSSAIN1
*1
Department of Physics, G.C. University, Faisalabad, Punjab, Pakistan
2
PSO, Nuclear Institute of Agriculture and Biology (NIAB), Faisalabad, Punjab, Pakistan
*Corresponding author’s email: profkhan786@yahoo.com
*Corresponding Author’s Cell No. +92-0302-6062879
Abstract
In this study the assay of labeled pesticide treated plants (Wheat and Maize), the major
crops of Punjab was performed using biological oxidizers Soxhlet extraction operators and
scintillation counting assembly. The data received after the treatment the wheat and maize
plants with C14 the measured radioactivity showed that greater content was accumulated in
the wheat root (0.15μCi), medium in leaves (0.10μCi) and least in stem (0.07μCi). While in
case of Maize the order of accumulation was found to be greater in leaves (0.14μCi),
medium in root (0.12μCi) and least in stem portion (0.08μCi) respectively. Data also
revealed that Maize showed more absorption capability of pesticides as compared to Wheat
which is more probability due to large fat contents and high transpiration rate (Higher be
the nuclear area of cross section more be the probability of absorption). It is strongly
recommended that use of pesticide Maize should be minimized to overcome the hazardous
effects on humans, animals, plants and eco-system disturbance.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
47
Keywords:
Malathion, C14 labeled Wheat, Maize plants, Biological oxidizers, scintillation counter,
maize more absorptive than wheat, reduced pesticide spray, health hazards, protective
measures
Introduction
Radiation affects the growth rate and germination percentage of crop seeds and also genetic
variations can also be made through irradiation process. In recent years, ionizing radiation
has been used successfully to bring about genetic variations in different crop species and is
considered as valuable tool for the improvement of different crop plants. The effects of
radiation on various crop plants have been reported by different authors throughout the
scientific world. Present work is a humble attempt in this regard (Abidi and Nizami, 1995;
Abbas et al., 2006; Adriyano et al., 2006).
Malathion is an organophosphate parasympathomimetic, which binds irreversibly to
cholinesterase. Malathion is an insecticide of relatively low human toxicity. In the former
USSR it was known as carbophos, in New Zealand and Australia as maldison and in South
Africa as mercaptothion. However, Malathion breaks down into malaoxon, which is 60
times more toxic than Malathion. For this reason, if Malathion is used or somehow enters
an indoor environment, as it breaks down into malaoxon, it can seriously and chronically
poison the occupants living or working in this environment. Malathion present in untreated
water is converted to malaoxon during the chlorination phase of water treatment, so
Malathion should not be used in waters that may be used as a source for drinking water, or
any upstream waters. In 1976, numerous malaria workers in Pakistan were poisoned by
isomalathion, a common impurity in Malathion, which is capable of inhibiting
carboxyesterase enzymes in those exposed to it; the original toxicity evaluation for
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
48
Malathion had not anticipated isomalathion co exposure (Halstead and Renni 2006;
Howard and Pelc 1953; Marshall and Wright 1998; Mumma and Hamilton 2003; Macias et
al, 2006; Nishikawa et al 1994; Ahmad, and Bhutta 2005).
Materials and Methods
Wheat (Triticum aestivum L.) and Maize (Zea mays L.) were taken as test plants in this study.
Seeds of Wheat and Maize were germinated in the clay pots by taking 500 g of soil in each pot.
Before the germination of seeds a pesticide labeled C14
(Malathion) of activity 0.4μCi was mixed in
the soil. Both the pots were placed in the laboratory. After 15 days plants were uprooted gently. The
healthy plants were weighed. The weight of the healthy plant of Maize was 500 mg and that of
Wheat plant was 3600mg. The parts (roots, stems and leaves) of the both plants were separated and
were dried in the oven at 50ºC for 24 hours and weighed. The weight of the Wheat roots, stem and
leaves was 530mg, 850mg and 960mg, respectively. Similarly the weight of Maize roots, stem and
leaves was 150mg, 130mg and 120mg, respectively. The weight of the each sample of soil was
taken as 500mg. The samples were put into cone and formed a pallet. Then these samples were
combusted in the Harry Biological oxidizer Model Ox-600 and C14
was trapped by the trap solution
(Ethanol amine+ Methanol). The trap solution was taken in the 20ml glass scintillation vial
(Packard, USA) and mixed with scintillation cocktail (Ahmad, 2005). Scintillation solution was
prepared by dissolving 4g of PPO (2, 5-diphenyloxazole) and 0.1g of POPOP [1, 4-bis- (5-
phenyloxazolyl)-benzene] Packard USA in 1 liter of Toluene (analytical grade) Merck Germany
(Laboratory training manual, IAEA, 1991). The vials were subjected to counting C14
activity using
a liquid scintillation counter (Nuclear Enterprises Model LSC1) shown in Figure 1 & 2 (Nilanjani
2006; Tarpely and Victor, 1997; Ahmad and Bhutta, 2005). The block diagram of the scintillation
counting assembly is shown in Fig 3.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
49
Fig. 1 Liquid scintillation counter
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
50
Fig. 2 Liquid scintillation vials
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
51
Photo multipliers Counting vial Photo multipliers
Coincidence
Pulse height analyzer
Scalar
Fig. 3. Block diagram of Liquid Scintillation Counter
Internal Standardization and instrument optimization
The counting is determined by counting the sample (Cs) and then adding a known amount
of activity (Di) and recounting (Cs+i). The added radioactive standard material must be
compatible with the sample Scintillator system and its absolute activity Di must be
accurately known. The counting efficiency є for the quenched sample is
ε = Cs+I / Di
The activity of quenched sample is thus
Ds = Cs / ε
Counting of the sample and recounting after addition of standard must be performed using
the same instrument for gain and window setting (Khan, 2003; Kazmi and Zada 2003).
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
52
Results and Discussion
Radiation and radioactive substances are natural and permanent features of the
environment, and thus the risks associated with radiation exposure can only be restricted,
not eliminated entirely. Additionally the man made radiation is wide spread. Sources of
radiation are essential to modern health care. Disposal medical supplies sterilized by
intense radiation have been central to combating disease.
Radiology is a vital diagnostic tool and radiotherapy is commonly part of the treatment of
malignancies. The use of nuclear energy and application of its by-products i.e., radiation
and radioactive substances, continue to increase around the world. Nuclear techniques are
in growing use in industry, agricultural, medicine and many fields of research, benefiting
hundreds of millions of people and giving employment to millions of people in the related
occupations.
Irradiation is used around the world to preserve foodstuffs and reduce wastage, and
sterilization techniques have been used to eradicate disease carrying insects and pests.
Industrial radiography is in routine use, for example to examine welds and detect cracks
and help prevent the failure of engineered structures.
In this study, the assay of labeled pesticides treated plant was performed using Biological
Oxidizer, Soxhlet Extraction Apparatus and Liquid Scintillation Counting techniques. The
plants (wheat and maize) treated with malathion (0.4 Ci) were harvested after 15 days and
separated to different parts i.e. roots, stems and leaves. The soil of both pots was
combusted and extracted using methanol as solvent and then noted the radioactivity by
liquid scintillation counting. The data of maize plant (root, stem and leaves) and soil
before and after harvesting the plant are given in Table1 and 3.
14
C-labelledmalathion (0.4µCi) was applied to soil and maize and wheat seeds were grown
in the treated soil. The applied labeled pesticide was systemic in nature and believed that it
may distribute and translocate to all parts of plants with in short interval of time.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
53
Radioactivity in maize plant and Soil
Table 1 summarizes the total DPM and activity found in different parts of plant. A major
portion of the total activity was restricted in leaves of maize (34%) of the applied activity
but least was found in stem part (20%). Our results are in accordance with the earlier
reported investigations.
Root of maize plant was combusted using Biological Oxidizer and the 14
CO2 was trapped
in trapping solution and mixed with Scintillator. The activity was determined using
scintillation counter and found reasonable activity in this part of plant (29.75%). From the
data it is evident that the activity translocated to every part of plant with in 15 days. Our
results were agreed with (Harhash et al., 2007). They conducted the fate of labeled
fungicide in bean plants with high application rate (2mCi/g).
The soil of maize treated plant was assayed for radioactivity before and after the plant
harvest. From the data it is clear that some portion of the labeled pesticide remained in soil
after 15 days. It is evident that labeled compound showed strong interactions with soil
fractions like humus. For mass balance the soil was combusted and extracted in methanol.
After careful observations, it was found that substantial portion of the activity was retained
in soil (31.72%). The data are shown in Table 1 Our results are in agreement with (Zhang
et al., 1989). The data of graphical presentation and activity in maize parts and soil is
given in Table 2 and illustrated in graph 1 respectively.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
54
Table 1 Assay of radioactivity of maize by liquid scintillation counter
Sr
. #
Sample
of Maize
CPM Average
CPM
DPM 95%
Efficienc
y
Total DPM Activity
(µ Ci)
1 2 3
1. Root 37
5
38
6
36
2
374.333
3
456.851
3
529.6816 264840.799
9
0.11929
8
2. Stem 24
0
25
5
26
0
251.666
7
307.144 356.1083 178054.144
2
0.08020
5
3. Leaves 46
5
48
6
41
5
455.333
3
555.707 644.2966 322148.292
7
0.14511
2
4. Soil
before
plantatio
n
98
0
97
2
96
5
972.333
3
1186.67
4
1375.851 687925.746
6
0.30987
6
5. Soil after
plantatio
n
36
5
41
0
42
0
398.333
3
486.141
9
563.6416 281820.797
8
0.12694
6
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
55
Table 2 Fate of C14
radioactivity in maize and soil
Table 3 Assay of radioactivity of wheat by liquid scintillation counter
Sr. # Sample
of
Wheat
CPM
Averag
e CPM
DPM 95%
Efficien
cy
Total
DPM
Activity
(µ Ci)
1 2 3
1. Root 485 490 488 487.666
7
595.167
8
690.048
2
345024.
1232
0.15541
6
2. Stem 245 235 260 246.666
7
301.041
8
349.033
3
174516.
6447
0.07861
1
Sr. #
Sample Name Activity (µ Ci)
1. Root 0.12
2. Stem 0.08
3. Leaves 0.14
4. Soil before plantation 0.31
5. Soil after plantation 0.12
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
56
3. Leaves 336 320 328 328 400.304
3
464.119
9
232059.
9707
0.10453
2
4. Soil
before
plantati
on
976 968 982 975.333
3
1190.33
6
1380.09
6
690048.
2463
0.31083
3
5. Soil
after
plantati
on
450 415 425 430 524.789
1
608.449
9
304224.
9617
0.13703
8
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
57
Table 4 Fate of C14
radioactivity in wheat and soil
The data of residue present in wheat plant (root, stem and leaves) and soil before and after
harvesting the plant is given in Table 3, 4.
Radioactivity in wheat plant and Soil
Table summarizes the total DPM and 14
C-activity found in different parts of plant. A major
portion of the total activity was restricted in leaves of wheat (26.13%) of the applied
activity but least was found in stem part (19.65%). Our results are in accordance with the
Sr.# Sample Name Activity
(µ Ci)
1. Root 0.15
2. Stem 0.07
3. Leaves 0.10
4. Soil before
plantation
0.31
5. Soil after
plantation
0.13
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
58
earlier reported investigations (Ahad et al., 2000). Root of wheat plant was combusted
using Biological Oxidizer and the 14
CO2 was trapped in trapping solution and mixed with
scintillator. The activity was determined using scintillation counter and found reasonable
activity in this part of plant (38.85%). From the data it is evident that the activity was
translocated to every part of plant with in 15 days. The results of (Agarwal and Rao 1998;
Kiml et al 2004) also supported to our results. They concluded the fate of labeled fungicide
in brinjal plants with high application rate (2.5mCi/g).
The soil of wheat treated plant was assayed for radioactivity before and after plant
harvesting. From the data (Table 3 and 4) it is evident that some portion of the labeled
pesticide remained in soil after 15 days. It is true that labeled compound showed strong
interactions with soil fractions like humus. For mass balance, the soil was combusted and
extracted in methanol. After careful observations, it was found that substantial portion of
the activity was retained in soil (34.25%). The data are shown in Table 3. Our results are in
agreement with Zhang et al., 1989. The data of graphical presentation and activity in wheat
parts and soil is given in Table 4 and illustrated in Graph 2 respectively.
Conclusions
From the results it is evident that maize showed more absorption of labelled pesticide as
compared to wheat. It may be due to its greater fat content and high transpiration rate. The
labeled pesticide got conjugation with fatty acid molecule and persistent longer time that
why the residue of pesticide is higher as compared to wheat crop. From the result it is
recommended that use of pesticide on this crop may be minimized.
CO2 is essential for photosynthesis because plants prepare Carbohydrates through its
fixation. This study also shows that roots absorb the same amount of CO2 which is due to
the application of C14
as an indicator. Absence of CO2 in the stem indicates that the
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
59
glucose in the roots splits into CO2 and H2O. Some of CO2 was absorbed by the roots and
the remaining was up taken by the leaves.
This absorption and distribution may create health hazards for human beings and animals
through the food chain, vegetables and fruits. For that purpose, survey was conducted and it
was found that for the time being, there is no danger for human beings but it has mild
symptoms in animals (Ahmad and Iram, 2005; Ahmad and Bhutta, 2005; Appleton, 1964;
Rabidean, G.S. and L.W. Mericle. 1980; Scheunert, 1990; Schreiber, L. and J. Schonberr.
1992; Cohen, Y. and U. Gisi. 1993; ).
References:
Abbas, Y., M. Ducousso, M. Abourouh, R. Azcon and R. Duponnois. 2006.
Diversity of arbuscular mycorrhizal fungi in Tetraclinis articulata (Vahl). Annals of
Forest Science 63(3): 285-291.
Abidi, S.M.A. and W.A. Nizami. 1995. [3
H] Amino acid uptake and metabolic
studies on Gigantocotyle explanatum and gastrothylax cruminefer (degenea
perpendicular to, paraphistomidae). International Journal for Parasitology 25(5):
541-549.
Adriano-Anaya, M.L., M. Salvador-Figueroa, J.A. Ocampo, I. Garcia-Romera.
2006. Hydrolytic enzyme activities in maize (Zea mays) and sorghum (Sorghum
bicolor) roots inoculated with Gluconacetobacter diazotrophicus and Glomus
intraradices. Soil Biology & Biochemistry 38(5): 879-886.
Agarwal S, Rao AV. 1998. Tomato oxidation: a human dietary intervention study.
Lipids 33: 981–984.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
60
Ahad, K., T. Anwar, I. Ahmad, A. Mohammad, S. Tahir, S. Aziz, and U.K. Baloch.
2000. Determination of pesticide residues in ground water of Mardan Division,
NWFP, Pakistan. J. Water (South Africa), 26 (3): 409 – 412.
Ahmad, I. 2005. Role of Biotechnology in Plant Pathology. In: A Text Book of
Introductory Plant Pathology. National Book Foundation, Islamabad, Pakistan, Eds.
I. pp. 357-73.
Ahmad, I. and A.R. Bhutta. 2005. Potato Crop Health Management through IPM
Approach. In: Seed Potato Crop Management in Northern Areas. Federal Seed
Certification and Registration Department & Department of Agriculture, Northern
Areas.
Ahmad, I. and S. Iram. 2005. Potato Crop Health Management through IPM
Approach. IPEP, NARC – Department of Mycology and Plant Pathology,
University of Punjab, Lahore.25 p.
Appleton, T.C. 1964. Autoradiography of soluble labeled compounds. F. Rog Micr
Soc 83: 277-282.
Cohen, Y. and U. Gisi. 1993. Uptake translocation and degradation of C-14
cymoxanil in tomato plants. Crop Protection 12(14): 284-292.
Halstead, E.H. and D.A. Rennie. 1984. The movement of injected P-32 through out the
wheat plant. Can. J. Bot 43: 1359-66.
Harhash, M.M. and R.S. Al-Obeed. 2007. Effect of naphthalene acetic acid on yield
and fruit quality of barhee and shahl date palm cultivars. Assiut J. of Agric. Sci.
38(2): 63-73.
Howard, A. and S.R. Pelc. 1953. Synthesis of deoxyribo nucleic acid in the normal
and irradiated cells and its relation to chromosome breakage. Heredity 6: 261-73.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
61
Kazmi, M.R. and R. Zada. 2003. Facilitating Scientific Methods (How to work with
Post-FFS Groups). Published by National IPM Programme, Pakistan Agricultural
research Council, Islamabad, Pakistan. 24 p.
Khan, M.A., I. Ahmad, N.I. Hashmi and M.A. Matin. 2003. Strategic Environment
for Research: Environment Analyses and Strategy for National Agricultural
Research Centre, Islamabad, Pakistan. PARC-ISNAR. ISBN No.969-409-161-
6.p.100.
Kim1, Y., R. DiSilvestro1, and S. Clinton1. 2004. Effects of Lycopene-beadlet or
tomato-powder feeding on carbon tetrachloride-induced hepatotoxicty in rats.
Phytomedicine 11: 152–156, 2004 http://www.elsevier-deutschland.de/phymed
Marshall, A.T. and A. Wright. 1998. Coral calcification autoradiography of a
scleractinian coral Galaxea Fasciculiris after incubation in Ca-45 and C-14. Coral
Reefs 17(1): 37-47.
Mumma, R.O. and R.H. Hamilton. 2003. Advances in pesticide metabolite through
the use of plant tissue cultures. J. Chemo sphere 12(5): 943-953.
Nilanjani, S., P.S. Kumari and C. Ashim. 2006. Laboratory simulated dissipation of
metasulfuron methyl and chlorimuron ethyl in soils and their residual fate in rice,
wheat and soybean at harvest. Can. J. Bot 36: 1259-66.
Nishikawa, N., S. Toyama, A. Shida and F. Futatesuya. 1994. The uptake and the
transport of C-14 Labeled Epibrassinolide in intact seedlings of cucumber and
wheat. J. Plant Research 107(1086): 125-30.
Rabidean, G.S. and L.W. Mericle. 1980. The distribution of C-14 in the root, shoot apices
of young corn plants. Plant Physiology 28: 329-33.
Scheunert, I., C. Marra, R. Wiswanathan, W. Klien and F. Korte. 1990. Fate of C-
14 labeled hexachlorobenzene in wheat plants and soil under outdoor conditions. J.
Chemo sphere 12(6): 843-53.
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
62
0
0.1
0.2
0.3
0.4
µCi
Activity
Roo
Activity in
Stem
Activity in
Leave
Activity in
Soil BP
Activity in
Soil AP
Fate of Radioactivity in Maize and Soil
Schreiber, L. and J. Schonberr. 1992. Analysis of foliar uptake of pesticides in
barley leaves: role of epicuticular waxes and compartmentation. Pesticide Science
36(3): 213-21.
Tarpely, L. and D.M. Victor. 1997. Differential autoradiography and Spin column
purification of sugars on activated charcoal. J. Crop. Science 37(6): 1807-11.
Zhang, W. R., Chen, S. S., and Besdek, J. C. (1989) Pool 2: a generic system for
cognitive map development and decision analysis. IEEE Transactions on Systems,
Man and Cyber-netics, 19, 31±39.
Graph. 1 Fate of Radioactivity in Maize and Soil
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
63
0
0.05
0.1
0.15
0.2
0.25
0.3
0.35
µCi
Activity in
Root
Activity in
Stem
Activity in
Leaves
Activity in
Soil BP
Activity in
Soil AP
Fate of Radioactivity in Wheat and Soil
Graph. 2 Fate of Radioactivity in Wheat and Soil
AUTHOR,S PROFILE:
Dr Khan has received his M.Phil Degree in Solid State Physics from CSSP (PU) Lahore
Pakistan with research project entitled “Radioactive Pollution and its Health Hazards, a
Study by SSNTDs and XRD analysis” and Master Degree in Physics with specialization in
“Advance Electronics” from G.T.I.College (new Campus) Rabwah, PAKISTAN affiliated with
PU, Lahore. Recently has completed his PhD Degree with project in Solid State Physics
entitled “A Comprehensive Investigation of Solid Aerosols Using XRD and ASS Techniques”
He has completed other relevant Post graduate training courses as participant, presenter
and as a faculty member in his areas of specialization from PINUM, NIAB, PNRA, NIFA, EPD
etc the well reputed institutions of Pakistan Atomic Energy Commission and Environmental
Protection Department along with his Professional in service training. Recently He is
working as Associate Professor of Physics in the Department of Physics GCU (UDC/CC)
ISSN: 2348 9510
International Journal Of Core Engineering & Management(IJCEM)
Volume 1, Issue 3, June 2014
64
Faisalabad. As for as his research Experience is concerned it is multidimensional, He has
more than 30 years of academic and research experience at graduation and post graduation
level, his areas of interest are Solid state Physics, Surface Physics, Aerosol Physics, Thin
Film Technology, Crystal Growth, Cloud Nucleation Theory, Nano Physics Atomic and
Nuclear Physics, Health and Medical Physics, Radiation Physics, Radiography and Medical
Imaging Geo Physics, Soil Physics, Climatology and Meteorology, X-ray Crystallography etc.
More than 95 Research Projects have been completed under his supervision with breakup
as Atomic and Environmental research Project Physics (33), Health and Medical Physics
(12), Radiation Physics and Dosimetery (33), Solid State Physics “ Electronics and Electrical
Instrumentation (09), Soil and Geo Physics (05), Laser and Plasma Physics (03) respectively
and have 95 research publications along with 20 manuscripts in progress and expected to
be published very soon in well reputed journals in his credit, He is Ex. Pakistan Nuclear
Regularity Authority (PNRA) certified Health Physicist RPO, RSO (PAEC) as attachment with
atomic and Nuclear Physics research lab. Editor ,executive editor ,associate editor Active
member of advisory boards, Editorial Committee and reviewer/ referee in above said areas
of interest for more than 15 national international journals Dr Khan has also honored to be
a member of world class societies, institutes, webs, organizations and important links
related to his areas of specialization like Prof. Abdul Salam Physics Society, Pakistan
Institute of Physics (PIP), Physics web (the community websites of Institute of Physics),
Nanotech web org. (the community websites of Institute of Physics), Medical Physics web
(the community websites of Institute of Physics), Optics org. (The community websites of
Institute of Physics), PASTIC. (Pakistan Science Foundation), the Aerosol Society” the
science of airborne particles, USA. American Association of Physics Teachers (AAPT).
American Physics Society (APS), Particle and High energy physics, global research and
consulting network, Radiation protection and Dosimetry (RPD), Saudi medical physics
society (SMPS), African Physical society (AFPS), American Association of Physicist in
medicine (AAPM),

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Diverse distribution-study-of-c-14-through-out-the-major-crops-of-punjab-pakistan-using-biological-oxidizer-and-liquid-scintillation-counter

  • 1. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 46 Diverse Distribution Study Of C-14 Through Out The Major Crops Of Punjab (Pakistan) Using Biological Oxidizer And Liquid Scintillation Counter MUHAMMAD ATTIQUE KHAN SHAHID1* , IJAZ AHMAD KHAN1 , SAEED AHMAD1 , MUHAMMAD RAFIQUE AASI2 , TAQMEEM HUSSAIN1 *1 Department of Physics, G.C. University, Faisalabad, Punjab, Pakistan 2 PSO, Nuclear Institute of Agriculture and Biology (NIAB), Faisalabad, Punjab, Pakistan *Corresponding author’s email: profkhan786@yahoo.com *Corresponding Author’s Cell No. +92-0302-6062879 Abstract In this study the assay of labeled pesticide treated plants (Wheat and Maize), the major crops of Punjab was performed using biological oxidizers Soxhlet extraction operators and scintillation counting assembly. The data received after the treatment the wheat and maize plants with C14 the measured radioactivity showed that greater content was accumulated in the wheat root (0.15μCi), medium in leaves (0.10μCi) and least in stem (0.07μCi). While in case of Maize the order of accumulation was found to be greater in leaves (0.14μCi), medium in root (0.12μCi) and least in stem portion (0.08μCi) respectively. Data also revealed that Maize showed more absorption capability of pesticides as compared to Wheat which is more probability due to large fat contents and high transpiration rate (Higher be the nuclear area of cross section more be the probability of absorption). It is strongly recommended that use of pesticide Maize should be minimized to overcome the hazardous effects on humans, animals, plants and eco-system disturbance.
  • 2. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 47 Keywords: Malathion, C14 labeled Wheat, Maize plants, Biological oxidizers, scintillation counter, maize more absorptive than wheat, reduced pesticide spray, health hazards, protective measures Introduction Radiation affects the growth rate and germination percentage of crop seeds and also genetic variations can also be made through irradiation process. In recent years, ionizing radiation has been used successfully to bring about genetic variations in different crop species and is considered as valuable tool for the improvement of different crop plants. The effects of radiation on various crop plants have been reported by different authors throughout the scientific world. Present work is a humble attempt in this regard (Abidi and Nizami, 1995; Abbas et al., 2006; Adriyano et al., 2006). Malathion is an organophosphate parasympathomimetic, which binds irreversibly to cholinesterase. Malathion is an insecticide of relatively low human toxicity. In the former USSR it was known as carbophos, in New Zealand and Australia as maldison and in South Africa as mercaptothion. However, Malathion breaks down into malaoxon, which is 60 times more toxic than Malathion. For this reason, if Malathion is used or somehow enters an indoor environment, as it breaks down into malaoxon, it can seriously and chronically poison the occupants living or working in this environment. Malathion present in untreated water is converted to malaoxon during the chlorination phase of water treatment, so Malathion should not be used in waters that may be used as a source for drinking water, or any upstream waters. In 1976, numerous malaria workers in Pakistan were poisoned by isomalathion, a common impurity in Malathion, which is capable of inhibiting carboxyesterase enzymes in those exposed to it; the original toxicity evaluation for
  • 3. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 48 Malathion had not anticipated isomalathion co exposure (Halstead and Renni 2006; Howard and Pelc 1953; Marshall and Wright 1998; Mumma and Hamilton 2003; Macias et al, 2006; Nishikawa et al 1994; Ahmad, and Bhutta 2005). Materials and Methods Wheat (Triticum aestivum L.) and Maize (Zea mays L.) were taken as test plants in this study. Seeds of Wheat and Maize were germinated in the clay pots by taking 500 g of soil in each pot. Before the germination of seeds a pesticide labeled C14 (Malathion) of activity 0.4μCi was mixed in the soil. Both the pots were placed in the laboratory. After 15 days plants were uprooted gently. The healthy plants were weighed. The weight of the healthy plant of Maize was 500 mg and that of Wheat plant was 3600mg. The parts (roots, stems and leaves) of the both plants were separated and were dried in the oven at 50ºC for 24 hours and weighed. The weight of the Wheat roots, stem and leaves was 530mg, 850mg and 960mg, respectively. Similarly the weight of Maize roots, stem and leaves was 150mg, 130mg and 120mg, respectively. The weight of the each sample of soil was taken as 500mg. The samples were put into cone and formed a pallet. Then these samples were combusted in the Harry Biological oxidizer Model Ox-600 and C14 was trapped by the trap solution (Ethanol amine+ Methanol). The trap solution was taken in the 20ml glass scintillation vial (Packard, USA) and mixed with scintillation cocktail (Ahmad, 2005). Scintillation solution was prepared by dissolving 4g of PPO (2, 5-diphenyloxazole) and 0.1g of POPOP [1, 4-bis- (5- phenyloxazolyl)-benzene] Packard USA in 1 liter of Toluene (analytical grade) Merck Germany (Laboratory training manual, IAEA, 1991). The vials were subjected to counting C14 activity using a liquid scintillation counter (Nuclear Enterprises Model LSC1) shown in Figure 1 & 2 (Nilanjani 2006; Tarpely and Victor, 1997; Ahmad and Bhutta, 2005). The block diagram of the scintillation counting assembly is shown in Fig 3.
  • 4. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 49 Fig. 1 Liquid scintillation counter
  • 5. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 50 Fig. 2 Liquid scintillation vials
  • 6. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 51 Photo multipliers Counting vial Photo multipliers Coincidence Pulse height analyzer Scalar Fig. 3. Block diagram of Liquid Scintillation Counter Internal Standardization and instrument optimization The counting is determined by counting the sample (Cs) and then adding a known amount of activity (Di) and recounting (Cs+i). The added radioactive standard material must be compatible with the sample Scintillator system and its absolute activity Di must be accurately known. The counting efficiency є for the quenched sample is ε = Cs+I / Di The activity of quenched sample is thus Ds = Cs / ε Counting of the sample and recounting after addition of standard must be performed using the same instrument for gain and window setting (Khan, 2003; Kazmi and Zada 2003).
  • 7. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 52 Results and Discussion Radiation and radioactive substances are natural and permanent features of the environment, and thus the risks associated with radiation exposure can only be restricted, not eliminated entirely. Additionally the man made radiation is wide spread. Sources of radiation are essential to modern health care. Disposal medical supplies sterilized by intense radiation have been central to combating disease. Radiology is a vital diagnostic tool and radiotherapy is commonly part of the treatment of malignancies. The use of nuclear energy and application of its by-products i.e., radiation and radioactive substances, continue to increase around the world. Nuclear techniques are in growing use in industry, agricultural, medicine and many fields of research, benefiting hundreds of millions of people and giving employment to millions of people in the related occupations. Irradiation is used around the world to preserve foodstuffs and reduce wastage, and sterilization techniques have been used to eradicate disease carrying insects and pests. Industrial radiography is in routine use, for example to examine welds and detect cracks and help prevent the failure of engineered structures. In this study, the assay of labeled pesticides treated plant was performed using Biological Oxidizer, Soxhlet Extraction Apparatus and Liquid Scintillation Counting techniques. The plants (wheat and maize) treated with malathion (0.4 Ci) were harvested after 15 days and separated to different parts i.e. roots, stems and leaves. The soil of both pots was combusted and extracted using methanol as solvent and then noted the radioactivity by liquid scintillation counting. The data of maize plant (root, stem and leaves) and soil before and after harvesting the plant are given in Table1 and 3. 14 C-labelledmalathion (0.4µCi) was applied to soil and maize and wheat seeds were grown in the treated soil. The applied labeled pesticide was systemic in nature and believed that it may distribute and translocate to all parts of plants with in short interval of time.
  • 8. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 53 Radioactivity in maize plant and Soil Table 1 summarizes the total DPM and activity found in different parts of plant. A major portion of the total activity was restricted in leaves of maize (34%) of the applied activity but least was found in stem part (20%). Our results are in accordance with the earlier reported investigations. Root of maize plant was combusted using Biological Oxidizer and the 14 CO2 was trapped in trapping solution and mixed with Scintillator. The activity was determined using scintillation counter and found reasonable activity in this part of plant (29.75%). From the data it is evident that the activity translocated to every part of plant with in 15 days. Our results were agreed with (Harhash et al., 2007). They conducted the fate of labeled fungicide in bean plants with high application rate (2mCi/g). The soil of maize treated plant was assayed for radioactivity before and after the plant harvest. From the data it is clear that some portion of the labeled pesticide remained in soil after 15 days. It is evident that labeled compound showed strong interactions with soil fractions like humus. For mass balance the soil was combusted and extracted in methanol. After careful observations, it was found that substantial portion of the activity was retained in soil (31.72%). The data are shown in Table 1 Our results are in agreement with (Zhang et al., 1989). The data of graphical presentation and activity in maize parts and soil is given in Table 2 and illustrated in graph 1 respectively.
  • 9. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 54 Table 1 Assay of radioactivity of maize by liquid scintillation counter Sr . # Sample of Maize CPM Average CPM DPM 95% Efficienc y Total DPM Activity (µ Ci) 1 2 3 1. Root 37 5 38 6 36 2 374.333 3 456.851 3 529.6816 264840.799 9 0.11929 8 2. Stem 24 0 25 5 26 0 251.666 7 307.144 356.1083 178054.144 2 0.08020 5 3. Leaves 46 5 48 6 41 5 455.333 3 555.707 644.2966 322148.292 7 0.14511 2 4. Soil before plantatio n 98 0 97 2 96 5 972.333 3 1186.67 4 1375.851 687925.746 6 0.30987 6 5. Soil after plantatio n 36 5 41 0 42 0 398.333 3 486.141 9 563.6416 281820.797 8 0.12694 6
  • 10. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 55 Table 2 Fate of C14 radioactivity in maize and soil Table 3 Assay of radioactivity of wheat by liquid scintillation counter Sr. # Sample of Wheat CPM Averag e CPM DPM 95% Efficien cy Total DPM Activity (µ Ci) 1 2 3 1. Root 485 490 488 487.666 7 595.167 8 690.048 2 345024. 1232 0.15541 6 2. Stem 245 235 260 246.666 7 301.041 8 349.033 3 174516. 6447 0.07861 1 Sr. # Sample Name Activity (µ Ci) 1. Root 0.12 2. Stem 0.08 3. Leaves 0.14 4. Soil before plantation 0.31 5. Soil after plantation 0.12
  • 11. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 56 3. Leaves 336 320 328 328 400.304 3 464.119 9 232059. 9707 0.10453 2 4. Soil before plantati on 976 968 982 975.333 3 1190.33 6 1380.09 6 690048. 2463 0.31083 3 5. Soil after plantati on 450 415 425 430 524.789 1 608.449 9 304224. 9617 0.13703 8
  • 12. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 57 Table 4 Fate of C14 radioactivity in wheat and soil The data of residue present in wheat plant (root, stem and leaves) and soil before and after harvesting the plant is given in Table 3, 4. Radioactivity in wheat plant and Soil Table summarizes the total DPM and 14 C-activity found in different parts of plant. A major portion of the total activity was restricted in leaves of wheat (26.13%) of the applied activity but least was found in stem part (19.65%). Our results are in accordance with the Sr.# Sample Name Activity (µ Ci) 1. Root 0.15 2. Stem 0.07 3. Leaves 0.10 4. Soil before plantation 0.31 5. Soil after plantation 0.13
  • 13. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 58 earlier reported investigations (Ahad et al., 2000). Root of wheat plant was combusted using Biological Oxidizer and the 14 CO2 was trapped in trapping solution and mixed with scintillator. The activity was determined using scintillation counter and found reasonable activity in this part of plant (38.85%). From the data it is evident that the activity was translocated to every part of plant with in 15 days. The results of (Agarwal and Rao 1998; Kiml et al 2004) also supported to our results. They concluded the fate of labeled fungicide in brinjal plants with high application rate (2.5mCi/g). The soil of wheat treated plant was assayed for radioactivity before and after plant harvesting. From the data (Table 3 and 4) it is evident that some portion of the labeled pesticide remained in soil after 15 days. It is true that labeled compound showed strong interactions with soil fractions like humus. For mass balance, the soil was combusted and extracted in methanol. After careful observations, it was found that substantial portion of the activity was retained in soil (34.25%). The data are shown in Table 3. Our results are in agreement with Zhang et al., 1989. The data of graphical presentation and activity in wheat parts and soil is given in Table 4 and illustrated in Graph 2 respectively. Conclusions From the results it is evident that maize showed more absorption of labelled pesticide as compared to wheat. It may be due to its greater fat content and high transpiration rate. The labeled pesticide got conjugation with fatty acid molecule and persistent longer time that why the residue of pesticide is higher as compared to wheat crop. From the result it is recommended that use of pesticide on this crop may be minimized. CO2 is essential for photosynthesis because plants prepare Carbohydrates through its fixation. This study also shows that roots absorb the same amount of CO2 which is due to the application of C14 as an indicator. Absence of CO2 in the stem indicates that the
  • 14. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 59 glucose in the roots splits into CO2 and H2O. Some of CO2 was absorbed by the roots and the remaining was up taken by the leaves. This absorption and distribution may create health hazards for human beings and animals through the food chain, vegetables and fruits. For that purpose, survey was conducted and it was found that for the time being, there is no danger for human beings but it has mild symptoms in animals (Ahmad and Iram, 2005; Ahmad and Bhutta, 2005; Appleton, 1964; Rabidean, G.S. and L.W. Mericle. 1980; Scheunert, 1990; Schreiber, L. and J. Schonberr. 1992; Cohen, Y. and U. Gisi. 1993; ). References: Abbas, Y., M. Ducousso, M. Abourouh, R. Azcon and R. Duponnois. 2006. Diversity of arbuscular mycorrhizal fungi in Tetraclinis articulata (Vahl). Annals of Forest Science 63(3): 285-291. Abidi, S.M.A. and W.A. Nizami. 1995. [3 H] Amino acid uptake and metabolic studies on Gigantocotyle explanatum and gastrothylax cruminefer (degenea perpendicular to, paraphistomidae). International Journal for Parasitology 25(5): 541-549. Adriano-Anaya, M.L., M. Salvador-Figueroa, J.A. Ocampo, I. Garcia-Romera. 2006. Hydrolytic enzyme activities in maize (Zea mays) and sorghum (Sorghum bicolor) roots inoculated with Gluconacetobacter diazotrophicus and Glomus intraradices. Soil Biology & Biochemistry 38(5): 879-886. Agarwal S, Rao AV. 1998. Tomato oxidation: a human dietary intervention study. Lipids 33: 981–984.
  • 15. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 60 Ahad, K., T. Anwar, I. Ahmad, A. Mohammad, S. Tahir, S. Aziz, and U.K. Baloch. 2000. Determination of pesticide residues in ground water of Mardan Division, NWFP, Pakistan. J. Water (South Africa), 26 (3): 409 – 412. Ahmad, I. 2005. Role of Biotechnology in Plant Pathology. In: A Text Book of Introductory Plant Pathology. National Book Foundation, Islamabad, Pakistan, Eds. I. pp. 357-73. Ahmad, I. and A.R. Bhutta. 2005. Potato Crop Health Management through IPM Approach. In: Seed Potato Crop Management in Northern Areas. Federal Seed Certification and Registration Department & Department of Agriculture, Northern Areas. Ahmad, I. and S. Iram. 2005. Potato Crop Health Management through IPM Approach. IPEP, NARC – Department of Mycology and Plant Pathology, University of Punjab, Lahore.25 p. Appleton, T.C. 1964. Autoradiography of soluble labeled compounds. F. Rog Micr Soc 83: 277-282. Cohen, Y. and U. Gisi. 1993. Uptake translocation and degradation of C-14 cymoxanil in tomato plants. Crop Protection 12(14): 284-292. Halstead, E.H. and D.A. Rennie. 1984. The movement of injected P-32 through out the wheat plant. Can. J. Bot 43: 1359-66. Harhash, M.M. and R.S. Al-Obeed. 2007. Effect of naphthalene acetic acid on yield and fruit quality of barhee and shahl date palm cultivars. Assiut J. of Agric. Sci. 38(2): 63-73. Howard, A. and S.R. Pelc. 1953. Synthesis of deoxyribo nucleic acid in the normal and irradiated cells and its relation to chromosome breakage. Heredity 6: 261-73.
  • 16. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 61 Kazmi, M.R. and R. Zada. 2003. Facilitating Scientific Methods (How to work with Post-FFS Groups). Published by National IPM Programme, Pakistan Agricultural research Council, Islamabad, Pakistan. 24 p. Khan, M.A., I. Ahmad, N.I. Hashmi and M.A. Matin. 2003. Strategic Environment for Research: Environment Analyses and Strategy for National Agricultural Research Centre, Islamabad, Pakistan. PARC-ISNAR. ISBN No.969-409-161- 6.p.100. Kim1, Y., R. DiSilvestro1, and S. Clinton1. 2004. Effects of Lycopene-beadlet or tomato-powder feeding on carbon tetrachloride-induced hepatotoxicty in rats. Phytomedicine 11: 152–156, 2004 http://www.elsevier-deutschland.de/phymed Marshall, A.T. and A. Wright. 1998. Coral calcification autoradiography of a scleractinian coral Galaxea Fasciculiris after incubation in Ca-45 and C-14. Coral Reefs 17(1): 37-47. Mumma, R.O. and R.H. Hamilton. 2003. Advances in pesticide metabolite through the use of plant tissue cultures. J. Chemo sphere 12(5): 943-953. Nilanjani, S., P.S. Kumari and C. Ashim. 2006. Laboratory simulated dissipation of metasulfuron methyl and chlorimuron ethyl in soils and their residual fate in rice, wheat and soybean at harvest. Can. J. Bot 36: 1259-66. Nishikawa, N., S. Toyama, A. Shida and F. Futatesuya. 1994. The uptake and the transport of C-14 Labeled Epibrassinolide in intact seedlings of cucumber and wheat. J. Plant Research 107(1086): 125-30. Rabidean, G.S. and L.W. Mericle. 1980. The distribution of C-14 in the root, shoot apices of young corn plants. Plant Physiology 28: 329-33. Scheunert, I., C. Marra, R. Wiswanathan, W. Klien and F. Korte. 1990. Fate of C- 14 labeled hexachlorobenzene in wheat plants and soil under outdoor conditions. J. Chemo sphere 12(6): 843-53.
  • 17. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 62 0 0.1 0.2 0.3 0.4 µCi Activity Roo Activity in Stem Activity in Leave Activity in Soil BP Activity in Soil AP Fate of Radioactivity in Maize and Soil Schreiber, L. and J. Schonberr. 1992. Analysis of foliar uptake of pesticides in barley leaves: role of epicuticular waxes and compartmentation. Pesticide Science 36(3): 213-21. Tarpely, L. and D.M. Victor. 1997. Differential autoradiography and Spin column purification of sugars on activated charcoal. J. Crop. Science 37(6): 1807-11. Zhang, W. R., Chen, S. S., and Besdek, J. C. (1989) Pool 2: a generic system for cognitive map development and decision analysis. IEEE Transactions on Systems, Man and Cyber-netics, 19, 31±39. Graph. 1 Fate of Radioactivity in Maize and Soil
  • 18. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 63 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 µCi Activity in Root Activity in Stem Activity in Leaves Activity in Soil BP Activity in Soil AP Fate of Radioactivity in Wheat and Soil Graph. 2 Fate of Radioactivity in Wheat and Soil AUTHOR,S PROFILE: Dr Khan has received his M.Phil Degree in Solid State Physics from CSSP (PU) Lahore Pakistan with research project entitled “Radioactive Pollution and its Health Hazards, a Study by SSNTDs and XRD analysis” and Master Degree in Physics with specialization in “Advance Electronics” from G.T.I.College (new Campus) Rabwah, PAKISTAN affiliated with PU, Lahore. Recently has completed his PhD Degree with project in Solid State Physics entitled “A Comprehensive Investigation of Solid Aerosols Using XRD and ASS Techniques” He has completed other relevant Post graduate training courses as participant, presenter and as a faculty member in his areas of specialization from PINUM, NIAB, PNRA, NIFA, EPD etc the well reputed institutions of Pakistan Atomic Energy Commission and Environmental Protection Department along with his Professional in service training. Recently He is working as Associate Professor of Physics in the Department of Physics GCU (UDC/CC)
  • 19. ISSN: 2348 9510 International Journal Of Core Engineering & Management(IJCEM) Volume 1, Issue 3, June 2014 64 Faisalabad. As for as his research Experience is concerned it is multidimensional, He has more than 30 years of academic and research experience at graduation and post graduation level, his areas of interest are Solid state Physics, Surface Physics, Aerosol Physics, Thin Film Technology, Crystal Growth, Cloud Nucleation Theory, Nano Physics Atomic and Nuclear Physics, Health and Medical Physics, Radiation Physics, Radiography and Medical Imaging Geo Physics, Soil Physics, Climatology and Meteorology, X-ray Crystallography etc. More than 95 Research Projects have been completed under his supervision with breakup as Atomic and Environmental research Project Physics (33), Health and Medical Physics (12), Radiation Physics and Dosimetery (33), Solid State Physics “ Electronics and Electrical Instrumentation (09), Soil and Geo Physics (05), Laser and Plasma Physics (03) respectively and have 95 research publications along with 20 manuscripts in progress and expected to be published very soon in well reputed journals in his credit, He is Ex. Pakistan Nuclear Regularity Authority (PNRA) certified Health Physicist RPO, RSO (PAEC) as attachment with atomic and Nuclear Physics research lab. Editor ,executive editor ,associate editor Active member of advisory boards, Editorial Committee and reviewer/ referee in above said areas of interest for more than 15 national international journals Dr Khan has also honored to be a member of world class societies, institutes, webs, organizations and important links related to his areas of specialization like Prof. Abdul Salam Physics Society, Pakistan Institute of Physics (PIP), Physics web (the community websites of Institute of Physics), Nanotech web org. (the community websites of Institute of Physics), Medical Physics web (the community websites of Institute of Physics), Optics org. (The community websites of Institute of Physics), PASTIC. (Pakistan Science Foundation), the Aerosol Society” the science of airborne particles, USA. American Association of Physics Teachers (AAPT). American Physics Society (APS), Particle and High energy physics, global research and consulting network, Radiation protection and Dosimetry (RPD), Saudi medical physics society (SMPS), African Physical society (AFPS), American Association of Physicist in medicine (AAPM),