ASSESSMENT OF ORGANO-CLAY COMPLEX BEHAVIOR USING INFRARED TECHNIQUE

Document Type : Original Article

Abstract

ABSTRACT
The present study aims toassessment of organo- clay complex behavior using infrared (IR) technique. The results showed that the kaolinite clay mineral saturated with organic acids (humic and fulvic acids), Ca, Mg and Na cations, after the IR examination; the dominant active groups were: OH, N-H, C-H2, C=O, C=C, Al-O, Si-OH, C-C, Al-OH and C-H and the wavenumber were (3500-3670), (3400-3445), (2900-3000), (1620-1660), 1610, 1350, 1080, (950-1070), 850 and 810 cm-1 respectively.
Also the results  showed that the bentonite clay mineral impregnated with the same treatments and after examined by IR radiation that the active groups were:  OH, N-H, C=O, C=C, C-H, Si-O, C-C and Al-OH-Al and the wavenumber were (3250-3632), 3300, (950-1634), (1525-1631), (830-1068), (1048-1068), 1070 and (915-918) cm-1 respectively.
At the least, the arrangements of active groups on kaolinite mineral were as follows: OH > CH > Al-OH = C=O> N-H = C-C = CH2>C=C = Al-O = Si-OH. While the arrangements of active groups on bentonite mineral were as follows: OH > C=O = C=C>NH = CH>Si-O>Al-OH-Al>C-C.

Highlights

CONCLUSION

The results showed that the difference among the effective groups within the treatments of the one clay mineral is due to the prevailing cation type (Ca, Mg and Na) and behavior on element or clay mineral type. As for the difference in the effective groups between the treatment of the one mineral is due to the type of organic acid and its effects on the surface of clay mineral and the inner layers. While the difference of the effective groups between the minerals is due to the difference in the type of clay mineral (kaolinite and bentonite) and the group to which it belongs to.

Keywords

Main Subjects


 

Egypt. J. of Appl. Sci., 34 (11) 2019                                              373-386                                                 

 
ASSESSMENT OF ORGANO-CLAY COMPLEX BEHAVIOR USING INFRARED TECHNIQUE

Nabil, M.A. Bahnasawy

Soil Chem. and Phys. Dep., DRC, Egypt

Key Words:kaolinite, bentonite, humic acid, fulvic acid, IR and active groups

ABSTRACT

The present study aims toassessment of organo- clay complex behavior using infrared (IR) technique. The results showed that the kaolinite clay mineral saturated with organic acids (humic and fulvic acids), Ca, Mg and Na cations, after the IR examination; the dominant active groups were: OH, N-H, C-H2, C=O, C=C, Al-O, Si-OH, C-C, Al-OH and C-H and the wavenumber were (3500-3670), (3400-3445), (2900-3000), (1620-1660), 1610, 1350, 1080, (950-1070), 850 and 810 cm-1 respectively.

Also the results  showed that the bentonite clay mineral impregnated with the same treatments and after examined by IR radiation that the active groups were:  OH, N-H, C=O, C=C, C-H, Si-O, C-C and Al-OH-Al and the wavenumber were (3250-3632), 3300, (950-1634), (1525-1631), (830-1068), (1048-1068), 1070 and (915-918) cm-1 respectively.

At the least, the arrangements of active groups on kaolinite mineral were as follows: OH > CH > Al-OH = C=O> N-H = C-C = CH2>C=C = Al-O = Si-OH. While the arrangements of active groups on bentonite mineral were as follows: OH > C=O = C=C>NH = CH>Si-O>Al-OH-Al>C-C.

INTRODUCTION

The organic complexes of clay play an effective role in determining the characteristics of physical and chemical of soil and its relationship to plant nutrition, therefore their study is important to determines the impact of these characteristics and their roles in improving soil properties (FAO, 2000). The present study clearly demonstrates that FT-IR spectroscopy is an efficient method for the characterisation of the purified bentonite in an organic mixture. This is technique remains economical, rapid, and specific (Eisazadeh, et al. 2012) .Therefore, the identification of the adhesion of clay minerals to the predominant organic acids (humic and fulvic) and the difference between them increases the importance of these acids in influencing soil properties and the binding of the necessary cations (Balcke, et al. 2002).

 

374                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                              

 
The possibility of using pure clay minerals (kaolinite and bentonite) with organic acids (humic-fulvic), Ca, Mg and Na cations identify the effect of the type of cation or the type of organic acid on clay minerals and the group to which he belongs (Aderonke, et al. 2017).

Using infrared radiation is leach to reach the most suitable installation that improves soil properties and their agricultural development potentials(Balcke, et al. 2002). The chemical structure of humic and fulvic acids are shown in Fig. (1).

 

 (Humic acid)                                                        (Fulvic acid)

         mical formula C187H186O89N9S1                      Chemical formula C135H182O95N5S2

(Sam Boggs, et al. 1985).

Fig. (1) Chemical structure of humic and fulvic acids

Humic substances are considered as the most important constituents of soils (Sara et al. 2010). They form the largest fraction of soil organic matter and play the dominant role in improving soil productivity (Jayaganesh and Senthurpandian, 2010). Humic substances are formed by the decomposition of plant and animal residues by microorganisms (Rao et al. 2019). Organic matter is intrinsic essential components of all soils (FAO 2017). The humic and fulvic substances play an important role in increasing productivity and soil fertility (Khan et al. 2018).

The plant growth, improvement of tuber nutritive value and quality and improvement in tuber size and weight in potato plants co-inoculated with Bacillus strains and humic acid, a significant improvement was observed in potato production. Despite a low total tuber yield (28.3 t ha-1) in control treatment, combined inoculation increased potato production by around 140% which was with in the high range of the increase expected for both Bacillus strains and humic acid mono treatments. The stability and increased consistency of the potato plant response to bacterial inoculation in the presence of humic acid indicated a promising biotechnological tool to improve growth and adaptation of potatoes to field conditions  Ekin, (2019).

 

Egypt. J. of Appl. Sci., 34 (11) 2019                                                      375                                                 

 
Foliar application of FA has a significant beneficial influence on general quality of FCV tobacco of the SBCS region. Specifically, FA resulted in increased leaf K and reduced starch contents. Molecular analysis revealed that FA activated expression of high-affinity K transporters (enhanced K uptake), degraded stored starch, and energized plant metabolism (efflux of trios- PO4 for sucrose synthesis). We believe this is the first report on FCV tobacco grown on black soils that provides encouraging and consistent results that comprehensively highlight inclusive benefits of FA both from agronomic and molecular dimensions. Priya et al. (2014).

The present review was aimed to the technical procedural methods used by FT-IR for clay surface characterization because, FT-IR remain is an economical, rapid and common technique. A spectrum can be obtained in a few minutes and the instruments are sufficiently inexpensive as to be available in many laboratories according to Djomgoue and Njopwouo (2013).

Although there are different studies on the clay and organic matter complexes, they did not address the effective role of both fulvic and humic alone and their association with the cation structure on the surface of pure clay minerals to guide the importance of the type of clay minerals and their reciprocal cations in the reclaimed soil.

MATERIALS AND METHODS

Homoionic Clays

      Kaolinite and bentonite clays were purchased from Sigma-Aldrich Comp. Each of 10 g of clays was saturated with, Ca2+, Mg2+,and Na+ by five repeated treatments with 50 ml of 1M concentration of metal chloride. The cation-exchanged clays were thoroughly washed with water, and centrifuged for 10 min at 5000 rpm. The washing and centrifugation procedures were repeated until chloride ion was no longer detected by the AgNO3 test by FAO, (2008).

Extraction of humic and fulvic substances

Humic (HA) and fulvic (FA) acids were extracted from sheep manure according to the standard method described by Sánchez-Monedero et al. (2002). The manure was mixed with deionized water at a rate of 1:5 (w/v) and then treated with 0.5 N NaOH solution to extract the humic substances. Humic acid was separated from humus extract by acidification with 0.1 M HCl to reach a pH of 2.0, after being left over-night. The precipitate was collected and the supernatant was again adjusted to pH between 4.5 and 5 using NaOH solution. The fulvic acid fraction got was settled after 24 h. Both the humic substances and fulvic acid fractions were washed with distilled water to remove impurities. Finally, black coloured fine crystals of humic acid and brown coloured crystals of fulvic acid fractions were obtained.

 

376                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      

 
Preparation of organic clay complex

Organo clay complex will prepared by using two homoiconic clay for kaolinite and bentonite with (Ca, Mg, and Na) separately with humic and fulvic acids. Organic clay complex were prepared at ratio 1:100 following the procedure of Li et al., (2003) and Wang and Xing (2005). In brief, 0.5 g of HA and  FA were dissolved in a minimum volume of 0.5 M NaOH separately and stand overnight then up to 1000 ml to obtain final concentration, 500 mgl -1. The organic clay complex suspensions were intermittent shaking for one week. The sedimented particles were washed repeatedly with distilled water until no color, was seem in the supernatant. The washed organic clay complex was dried at 40 C, grounded and finally, passed through (170) mesh and sealed in the glass tube for use.

Infrared spectroscopy

The analysis of the infrared absorption of the pure clay minerals and  organic clay complex was carried out in KBr pellets using  Jasco FTIR-4100 from wavenumber 4000 to 400 cm-1 (Ma, et al. 2010).

RESULTS AND DISCUSSIONS

Infrared spectra of humic and fulvic acids are shown in Fig. (2) and Table (1). Humic acid show broad absorption centered around at 3360, 1406, 1233 and 1060 cm-1 regions (Edward et al., 2014). The phenolic (OH), amide, methyl, free-NH-bond, carboxylic and carbonyl group are presented in the humic and fulvic acids (Sharmah and Bordoloi, 1993). The absorption are around 1715 cm-1 region and due to the C=O stretching, (Haworth, 1971). The absorption are around 1630 cm-1 region that due to the C=C stretching vibrations of double bonds (Dorado et al., 2010). The 1200 cm-1 band is assigned to C-O stretching of phenols, carboxylic acids, ethers and OH- deformation of –COOH (Stevenson, 1994). The relative intensity of major IR absorption bands of humic and fulvic acids are shown in Table (1).

 

Egypt. J. of Appl. Sci., 34 (11) 2019                                                      377                                                 

 

              (Humic acid)                                        (Fulvic acid)    

Fig. (2) Infrared spectra of humic and fulvic acids

Table (1): Relative intensity of major IR absorption bands of humic and   fulvic acids

Acids

Frequency

(cm-1)

Assignment

Bond nature

 

 

 

 

Humic acid

3360

H-bonded OH, or free                                                     

Broad

2930

 C-H2 stretching

Weak

1715

C=O stretching

Weak

1630

C=C stretching vibration of double bonds

Shoulder

1406

Aliphatic C-H deformation

Medium

1233

 C-O stretching of phenols, carboxylic acids, ethers and  COOH groups 

Medium

1059

Si-O stretching

Weak

 

Fulvic

acid

3445

H-bonded OH, Free or bonded

Broad

1631

C=C stretching vibration

Strong

1404

 C-H

Weak

1068

Si-O stretching

Medium

 Jayaganesh and Senthurpandian (2010)

 

Kaolinite mineral

Figs. (3 and 4) and Table (2) shows that Kaolinite Clay- organic complexes can be attributed to kaolinite by IR absorption spectra. Their IR spectra demonstrate fully-represented and well-resolved OH, Al-O and Al-OH bands of the mineral lattice around 3650, 1350 and 850 cm-1 respectively. Kaolinite-Mg clearly-seen absorption bands of OH, Si-OH and Al-OH around 3500, 1080 and 850 cm-1 respectively. As the infrared absorption spectra showed, the kaolinite mineral adsorbed with humic acid is that the active groups are O-H stretching (H bonded OH group), N-H stretching, C-H2 stretching, C=O stretching of amide group and CH out of plane bending around wavenumber 3400, 2900, 1660 and 810 cm-1 respectively.  As for the kaolinite-humic-Mg, the dominant active groups were: OH, CH2 , C=C aromatic stretching and /or asymmetric –COO stretching, C-C stretching of aliphatic groups, C-O stretching of polysaccharides or polysaccharide-like, CH out of plane bending around the wavenumber  3680, 3000, 1620, 1070, 950, 810 and 775 cm-1 respectively.

 

378                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      

 

Fig. (3): Infrared spectra of Kaolinite Clay-Organic Complexes

 

Fig.(4) Kaolinite structure, showing the interlayer hydrogen bonds (Blanca, 2015)


Table (2): Infrared spectra of Kaolinite clay–Organic complexes

W.N.

(cm-1)

Kaolinite

W.N.

(cm-1)

Kaolinite- Mg

*W.N.

(cm-1)

Kaolinite -humic

W.N.

(cm-1

Kaolinite –humic-Mg

W.N.

(cm-1

Kaolinite fulvic-Na

W.N.

(cm-1

Kaolinite fulvic-Ca

W.N.

(cm-1

Kaolinite fulvic -Mg

3650

 

OH

Weak

3500

OH

Medium

3400

N-H stretching

Medium

3670

OH

Weak

3670

OH Stretching

Weak

3670

OH Stretching

Weak

3670

OH Stretching

Weak

1350

 

Al-O

Medium

1080

Si –OH Stretching

Strong

2900

C-H2 stretching

Weak

3000

C-H2

Broad

3445

N-H stretching

Weak

1620

C=O

Weak

1631

C=O stretching

Strong

850

 

Al-OH

Strong

850

Al-OH

Medium

1660

C=O stretching

Weak

1620

C=C stretching

Strong

810

CH

Weak

810

Weak

850

 

Al-OH

Weak

 

 

 

 

 

810

CH

Medium

1070

C-C Stretching

Weak

 

 

 

 

 

 

810

 

CH

Weak

 

 

 

 

 

 

 

950

C-O stretching

Weak

 

 

 

 

 

 

 

 

 

 

 

 

 

810

 

CH

Weak

 

 

 

 

 

 

 

 

*W.N= wavenumber

 


 

380                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      

 
However kaolinite mineral saturated with fulvic acid and sodium cation (kaolinite- fulvic-Na), the effective groups were OH stretching, N-H stretching and CH out of plane was bending around 3670, 3445 and 810 cm-1 respectively .While kaolinite saturated with fulvic acid and calcium cation (kaolinite-fulvic-Ca) the active groups were OH stretching, C=O, CH out of plane and CH out of plane bending around 3670, 1620, 810 and 810 cm-1 respectively. At least, kaolinite mineral saturated with fulvic acid and magnesium cation (kaolinite-fulvic-Mg), the effective groups were OH stretching, H-bending OH, free OH, intermolecular bonded OH, C=O stretching vibration of double bounds of cyclic and acyclic compounds benzene ring substitution around wavenumber 3670, 3500, 1631, 910 and 850 cm-1 respectively.    

Bentonite mineral

Figs. (5 and 6) and Table (3) shows that bentonite clay- organic complexes can be attributed to bentonite by IR absorption spectra. Their IR spectra demonstrate fully-represented and well-resolved OH stretching, H-bending OH, free OH, intermolecular bonded OH, C=O, Si-O stretching and Al-OH-Al bending   bands around wavenumber 3632, 3422, 1634, 1048 and 918  cm-1 respectively. Bentonite-Mg clearly-seen absorption bands of OH, C=O, Si-O stretching, Al-OH-Mg bending and Si-O stretching around 3250, 1634, 1048, 843 and 778 cm-1 respectfully. As the infrared absorption spectra showed, the bentonite mineral adsorbed with humic acid (bentonite-humic) that the active groups were N-H stretching, C=C aromatic stretching and /or asymmetric –COO stretching,-CH- polysaccharides, C=O stretching and CH out of plane around wavenumber 3300, 1600, 1050, 950 and 775 cm-1 respectively.  As for the bentonite-humic-Mg, the dominant active groups were: OH,  stretching, N-H stretching, C=C aromatic stretching and /or asymmetric –COO stretching, C-C stretching of aliphatic groups, C-O stretching of polysaccharides or polysaccharide-like, CH out of plane bending around the wavenumber  3600, 3300, 1620, 1070, 950, and 830 cm-1 respectively.

 However bentonite mineral saturated with fulvic acid and sodium cation (bentonite-fulvic-Na) the effective groups were  OH stretching, N-H stretching, C=C aromatic stretching, Si-O stretching, Al-OH-Al bending and Al-OH- around 3632, 3300, 1525, 1068, 915 and 842 cm-1 respectively. While bentonite saturated with fulvic acid and calcium cation (bentonite-fulvic- Ca) the active groups were OH stretching, C=C aromatic stretching and, CH out of plane around 3632, 1620, and 830 cm-1 respectively. At least, bentonite mineral saturated with fulvic acid and magnesium cation (bentonite-fulvic-Mg) indicated the effective groups were H-bonded OH, free OH, N-H stretching, C=C aromatic stretching, CH stretching, C=O stretching of polysaccharides or polysaccharide –like substances and CH out of plane around wavenumber 3400, 3300, 1631, 1068, 950 and 775 cm-1 respectively. 

 

Egypt. J. of Appl. Sci., 34 (11) 2019                                                      381                                                 

 

Fig.(5): Infrared spectra of Bentonite clay-organic complexes

 

Fig. (6) Bentonite structure, showing the interlayer hydrogen bonds (Jun, et al. 2019).


Table (3): Infrared spectra of Bentonite clay –Organic complexes

W.N.

(cm-1)

Bentonite

*W.N.

(cm-1)

Bentonite-Mg

W.N.

(cm-1)

Bentonite-Humic

W.N.

(cm-1

Bentonite-Humic-Mg

W.N.

(cm-1

Bentonite-Fulvic-Na

W.N.

(cm-1

Bentonite-Fulvic-Ca

W.N.

(cm-1

Bentonite-Fulvic-Mg

3632

OH stretching

Weak

3250

OH

Broad

3300

N-H stretching

Medium

3600

OH Stretching

Shoulder

3632

OH stretching

Weak

3632

OH Stretching

Shoulder

3400

OH Stretching

Shoulder

1634

C=O

Medium

1634

C=O

Strong

1600

C=C stretching

Medium

3300

N-H stretching

Broad

3300

N-H stretching

Medium

1620

C=C stretching

Weak

3300

N-H stretching

Broad

1048

 

Si-O stretching

Broad

1048

Si-O stretching

Weak

1050

-CH-

Shoulder

1620

C=C stretching

Medium

1525

C=C stretching

Medium

830

CH

Broad

1631

C=C stretching

Strong

918

 

Al-OH-Al bending

Weak

843

Al-OH- Mg bending

Medium

950

C=O stretching

Shoulder

1070

C-C Stretching

Shoulder

 

1068

Si-O stretching

Weak

 

 

1068

CH stretching

Shoulder

 

 

 

 

 

 

950

C-O stretching

Shoulder

915

Al-OH-Al bending

Shoulder

 

 

950

 

 

C=O stretching

Shoulder

 

 

 

 

 

 

 

 

 

830

CH

Shoulder

 

 

 

 

 

 

 

*W.N= wavenumber


 

Egypt. J. of Appl. Sci., 34 (11) 2019                                                      383                                                 

 

Assessment ofeffective groups

          Fig. (7) reveal a common of frequencyfunction groups on kaolinite mineral, dominated by OH, CH, C=O, Al-OH, N-H, CH2 , C-C, C=C, Al-O and Si-OH in a descending order.  While, contents of C=C, Al-O and Si-OH groups the least widespread.   

 

 Fig.(7) Frequency of function groups on kaolinite mineral

       Fig. 8 dictate that the frequency of function groups bentonite mineraldominant dominated by OH, C=O, C-C, N-H, CH, Si-O, Al-OH-Al and C-C in a descending order. It is noticeable; contents of C-C group the least common.

 

Fig. (8) Frequency of function groups bentonite mineral

        

CONCLUSION

The results showed that the difference among the effective groups within the treatments of the one clay mineral is due to the prevailing cation type (Ca, Mg and Na) and behavior on element or clay mineral type. As for the difference in the effective groups between the treatment of the one mineral is due to the type of organic acid and its effects on the surface of clay mineral and the inner layers. While the difference of the effective groups between the minerals is due to the difference in the type of clay mineral (kaolinite and bentonite) and the group to which it belongs to.

 

384                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      

 

REFERENCES

Aderonke, A.A. ; O.A. Idowu and S.B. Olugbenga (2017). Adsorption of dyes using different types of clay: a review. Appl Water Sci., 7:543–568.

Balcke, G.U. ; N.A. Kulikova ; S.F.D. Hesse ; I.V. Perminova and F.H. Frimmel (2002). Adsorption of humic substances onto kaolin clay related to their structural features. Soil Sci. Soc. Am. J., 6: 1805-1812.

Blanca, B.L.(2015). Halloysite and kaolinite: Two with geological and  technological importance . Rev. Real Acad. de Cie. Zara., 70: 1-33.

Dorado, F. ; P.B Garcia ; A. DeLucas ; M.J. Ramos and A. Romero (2010). Hydrocarbon selective catalytic reduction of No over Cu/Fe- pillared clays: diffuse reflectance infrared spectroscopy studies. J. Mol. Cata. A: Che., 332 (1-2): 45-52.

Djomgoue, P. and D. Njopwouo (2013).  FT-IR Spectroscopy Applied for Surface Clays Characterization.J. Surf. Eng.  Mater. and Adva. Tech., 3: 275-282.

Edward, W. ; S. Małgorzata ; K. Tomasz and R. Ewa (2014). The effect of dressing seed material with a humus preparation and foliar potassium Fertilization on the yield and chemical composition of spring barley grain.Acta Sci. Pol. Agric., 13(4): 153-162.

Eisazadeh, A. ; K.A. Kassim and H. Nur (2012). “Solid-state NMR and FTIR studies of lime stabilized montmorillonitic and lateritic clays,” Applied Clay Science,  67-68(5): 5–10.

Ekin, Z. (2019).Integrated Use of Humic Acid and Plant Growth Promoting Rhizobacteria to Ensure Higher Potato Productivity in Sustainable Agriculture. J. Sustain., 11:3417-3430.

FAO (2000). Guidelines and reference material on integrated soil and nutrient management and conservation for farmer field schools. 164 pp.

FAO (2008). Guide to laboratory establishment for plant nutrient analysis.Food and Agriculture Organization of the United Nations, Rome Fertilizer and Plant Nutrition bulletin 19.

 

Egypt. J. of Appl. Sci., 34 (11) 2019                                                      385                                                 

 

FAO (2017). Soil Organic Carbon: the hidden potential. Food and Agriculturer organization of the United Nations Rome, Italy.

Haworth, R.D. (1971). The chemical nature of humic acid. Soil Sci., 106: 188-192.

Jayaganesh, S. and V.K. Senthurpandian (2010). Extraction and Characterization of Humic and Fulvic acids from Latosols under Tea Cultivation in South India. Asian. J.  Ear. Sci., 3: 130-135.

Jun, Q. ; Li. Guoqing ; L. Dongliang ; J. Shan ; W. Guifang ; C. Ping ; Z. Xiangnan; Y. Geng ; L. Xiaodong and L. Xianjun (2019).Effect of Layer Charge Density on Hydration Properties of Montmorillonite: Molecular Dynamics Simulation and Experimental Study.  Int. J. Mol Sci., 20 (16): 3997.

Khan, R.U. ; M.Z. Khan ; A. Khan ; S. Saba ; F. Hussain and I.U. Jan (2018). Effect of humic acid on growth and crop nutrient status of wheat on two different soils. J. Plant Nutr., 41: 453–460.

Li, H.G. ; B. Sheng ; J. Teppen ; C.T. Johnston and S.A. Boyd (2003). Sorption and desorption of pesticides by clay minerals and humic acid-clay complexes. Soil Sci. Soci. of Ame. J., 67(1): 122-131.

Ma, Y. ; J. Zhu ; H. He ; P. Yuan ; W. Shen and D. Liu (2010). Infrared investigation of organo-montmorillonite prepared from different surfactants. Spectrochimica acta. Part A, Molecular and Biomolecular Spectroscopy., 76 (2): 122-129.

Rao, D.L.N. ; K.  Aparna and S.R.Mohanty (2019). Microbiology and Biochemistry of Soil organic matter, carbon sequestration and soil health. Ind. J.  Ferti., 15 (2): 124-138.

Priya, V.; K. Mahavishnan ; D. S. Gurumurthy and H. Bindumadhavah (2014).Fulvic Acid (FA) for Enhanced Nutrient Uptake and Growth: Insights from Biochemical and Genomic Studies.J. of Crop Improv., 28:740-757.

Sánchez-Monedero, M.A.; J.  Cegarra ; D. García and A. Roig (2002). Chemical  and structural evolution of humic acids during organic waste composting. Biodegradation., 13(6): 361-371.

Sara T. ; F. Ornella ; Q. Silvia  and N. Serenella (2010). Humic substances biological activity at the plant-soil interface. Plant Signal Behav., 5(6): 635-643.

 

386                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      

 

Sam Boggs, Jr. ; L. David and G. S.Martin (1985). Humic Substances in Natural Waters and their Complexation with Trace Metals and Radionuclides: A Review. Univ. of Oregon, Eugene, OR. Work performed under contract No. 31-109-38-7052.

Sharmah, A.C. and P.K. Bordoloi (1993). Characterisation of humic and fulvic acids extracted from two major soil groups of Assam. J. Indian Soc. Soil Sci., 41: 642-648.

Stevenson, F.J. (1994). Humus chemistry: genesis, composition, reactions. Wiley-Interscience, New York.

Wang, K. and B. Xing (2005). Structural and sorption characteristics of adsorbed humic acid on clay minerals. J,  Environ. Quality, 34(1): 342-349.

تقییم سلوک معقد الطین العضوى  بإستخدام نظام ألأشعه تحت الحمراء

نبیل محمد عبداللطیف بهنساوى

 قسم کیمیاء وطبیعة ألأراضى - مرکز بحوث الصحراء- مصر

          تهدف الدراسة إلى تقییم سلوک معقد الطین العضوى  بإستخدام نظام ألأشعه تحت الحمراء. وأوضحت النتائج أن معدن طین الکاؤلینیت المشبع بالأحماض العضویة وکاتیونات الکالسیوم والماغنسیوم والصودیوم بعد الفحص بالأشعة تحت الحمراء أن  المجامیع الفعاله السائدة هى:-                                      

 OH, N-H, CH2, C=O, C=C, Al-O, Si-OH, C-C, Al-OH and CHوذات أرقام موجیة هى: (3670-3500) ، (3445-3400) (3000-2900) ، (1660-1620) ، 1610، 1350، 1080، (1070-950) ، 850 و810 سم-1 على الترتیب.

کما أوضحت النتائج أن معدن طین البنتونیت المشبع بنفس المعاملات السابقة  بعد فحصها بالأشعة تحت الحمراء أن المجامیع الفعاله السائدة هى:-

 OH, N-H, and C=O, C=C, CH, Si-O C-C and Al-OH-Al وذات أرقام موجیة هى:

(3632-3250) ، 3300، (1634-950) ، (1631-1525) ، (1068-830 )  (1068-1048)،1070 و (918-915 )    سم-1على الترتیب.

ومن الدراسة إتضح أن ترتیب المجامیع الفعالة على معدن طین الکاؤلینیت کالتالى:-

OH > CH > Al-OH = C=O > N-H = C-C = CH2 > C=C = Al-O = Si-OH

بینما معدن طین البنتونیب فکان ترتیب المجامیع الفعالة هى:-

OH > C=O = C=C >NH = CH > Si-O >Al-OH-Al >C-C.

 
384                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      
 
REFERENCES
Aderonke, A.A. ; O.A. Idowu and S.B. Olugbenga (2017). Adsorption of dyes using different types of clay: a review. Appl Water Sci., 7:543–568.
Balcke, G.U. ; N.A. Kulikova ; S.F.D. Hesse ; I.V. Perminova and F.H. Frimmel (2002). Adsorption of humic substances onto kaolin clay related to their structural features. Soil Sci. Soc. Am. J., 6: 1805-1812.
Blanca, B.L.(2015). Halloysite and kaolinite: Two with geological and  technological importance . Rev. Real Acad. de Cie. Zara., 70: 1-33.
Dorado, F. ; P.B Garcia ; A. DeLucas ; M.J. Ramos and A. Romero (2010). Hydrocarbon selective catalytic reduction of No over Cu/Fe- pillared clays: diffuse reflectance infrared spectroscopy studies. J. Mol. Cata. A: Che., 332 (1-2): 45-52.
Djomgoue, P. and D. Njopwouo (2013).  FT-IR Spectroscopy Applied for Surface Clays Characterization.J. Surf. Eng.  Mater. and Adva. Tech., 3: 275-282.
Edward, W. ; S. Małgorzata ; K. Tomasz and R. Ewa (2014). The effect of dressing seed material with a humus preparation and foliar potassium Fertilization on the yield and chemical composition of spring barley grain.Acta Sci. Pol. Agric., 13(4): 153-162.
Eisazadeh, A. ; K.A. Kassim and H. Nur (2012). “Solid-state NMR and FTIR studies of lime stabilized montmorillonitic and lateritic clays,” Applied Clay Science,  67-68(5): 5–10.
Ekin, Z. (2019).Integrated Use of Humic Acid and Plant Growth Promoting Rhizobacteria to Ensure Higher Potato Productivity in Sustainable Agriculture. J. Sustain., 11:3417-3430.
FAO (2000). Guidelines and reference material on integrated soil and nutrient management and conservation for farmer field schools. 164 pp.
FAO (2008). Guide to laboratory establishment for plant nutrient analysis.Food and Agriculture Organization of the United Nations, Rome Fertilizer and Plant Nutrition bulletin 19.
 
Egypt. J. of Appl. Sci., 34 (11) 2019                                                      385                                                 
 
FAO (2017). Soil Organic Carbon: the hidden potential. Food and Agriculturer organization of the United Nations Rome, Italy.
Haworth, R.D. (1971). The chemical nature of humic acid. Soil Sci., 106: 188-192.
Jayaganesh, S. and V.K. Senthurpandian (2010). Extraction and Characterization of Humic and Fulvic acids from Latosols under Tea Cultivation in South India. Asian. J.  Ear. Sci., 3: 130-135.
Jun, Q. ; Li. Guoqing ; L. Dongliang ; J. Shan ; W. Guifang ; C. Ping ; Z. Xiangnan; Y. Geng ; L. Xiaodong and L. Xianjun (2019).Effect of Layer Charge Density on Hydration Properties of Montmorillonite: Molecular Dynamics Simulation and Experimental Study.  Int. J. Mol Sci., 20 (16): 3997.
Khan, R.U. ; M.Z. Khan ; A. Khan ; S. Saba ; F. Hussain and I.U. Jan (2018). Effect of humic acid on growth and crop nutrient status of wheat on two different soils. J. Plant Nutr., 41: 453–460.
Li, H.G. ; B. Sheng ; J. Teppen ; C.T. Johnston and S.A. Boyd (2003). Sorption and desorption of pesticides by clay minerals and humic acid-clay complexes. Soil Sci. Soci. of Ame. J., 67(1): 122-131.
Ma, Y. ; J. Zhu ; H. He ; P. Yuan ; W. Shen and D. Liu (2010). Infrared investigation of organo-montmorillonite prepared from different surfactants. Spectrochimica acta. Part A, Molecular and Biomolecular Spectroscopy., 76 (2): 122-129.
Rao, D.L.N. ; K.  Aparna and S.R.Mohanty (2019). Microbiology and Biochemistry of Soil organic matter, carbon sequestration and soil health. Ind. J.  Ferti., 15 (2): 124-138.
Priya, V.; K. Mahavishnan ; D. S. Gurumurthy and H. Bindumadhavah (2014).Fulvic Acid (FA) for Enhanced Nutrient Uptake and Growth: Insights from Biochemical and Genomic Studies.J. of Crop Improv., 28:740-757.
Sánchez-Monedero, M.A.; J.  Cegarra ; D. García and A. Roig (2002). Chemical  and structural evolution of humic acids during organic waste composting. Biodegradation., 13(6): 361-371.

Sara T. ; F. Ornella ; Q. Silvia  and N. Serenella (2010). Humic substances biological activity at the plant-soil interface. Plant Signal Behav., 5(6): 635-643.

 
386                                                      Egypt. J. of Appl. Sci., 34 (11) 2019                                                      
 
Sam Boggs, Jr. ; L. David and G. S.Martin (1985). Humic Substances in Natural Waters and their Complexation with Trace Metals and Radionuclides: A Review. Univ. of Oregon, Eugene, OR. Work performed under contract No. 31-109-38-7052.
Sharmah, A.C. and P.K. Bordoloi (1993). Characterisation of humic and fulvic acids extracted from two major soil groups of Assam. J. Indian Soc. Soil Sci., 41: 642-648.
Stevenson, F.J. (1994). Humus chemistry: genesis, composition, reactions. Wiley-Interscience, New York.
Wang, K. and B. Xing (2005). Structural and sorption characteristics of adsorbed humic acid on clay minerals. J,  Environ. Quality, 34(1): 342-349.