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Journal of Biology, Agriculture and Healthcare www.iiste.org
ISSN 2224-3208 (Paper) ISSN 2225-093X (Online)
Vol.4, No.24, 2014
147
Assessment of Some Micronutrient (Zn and Cu) Status of Fadama
Soils under Cultivation in Bauchi, Nigeria
Domchang Mamzing1
Nathan Akila Loks1
Williams Manggoel1
Selchak Boyi Gojing1
Stephen Azi Ashom2
1.Department of Agricultural Technology, College of Agriculture, PMB 001, Garkawa, Plateau State
2.Department of Animal Health and Production, College of Agriculture, PMB 001, Garkawa, Plateau State
Corresponding Author: williammanggoel@ymail.com
Abstract
The status of Zn and Cu of two fadama soils under cultivation at Lushi and Federal Low-cost Housing Estate in
Bauchi, Nigeria were determined between February and June, 2012. A total of 30 composite soil samples were
collected from 0-15cm, 15-30cm and 30-45cm depths from purposively selected representative locations in the
study area and analyzed using standard procedures. Particle size distribution of the soils showed clay loam
texture. Soil pH was strongly acidic with mean values of 5.36 and 5.59 for Lushi and Federal Low-cost soils,
respectively. Low levels of organic carbon (OC), available P, and exchangeable bases were observed. Though,
soil content of Zn and Cu were low, values increased significantly (p<0.05) with soil depths at both Lushi and
Federal Low-cost locations. The low mean values of these micronutrients at both Lushi (Zn=1.36mgKg-1
;
Cu=0.83mgKg-1
) and Federal Low-cost (Zn=1.32mgKg-1
; Cu=0.83mgKg-1
) implied that soil amendments of Zn
and Cu and/or application of appropriate quantities of key nutrient elements would enhance their availability for
optimum yields of crops for the resource-poor farmer in the study area.
Keywords: Micro nutrients, zinc, copper, fadama soils
1. Introduction
Micronutrients, though required in small quantities, are essential for the growth and development of crops. The
availability of these elements in correct amounts and proportions play a vital role in the absorption of other
nutrient elements, especially nitrogen, phosphorus and potassium. Micronutrients content of soils depends upon
the soil types, parent material, soil pH, organic matter, clay content, amount of exchangeable bases and
phosphate (Macias, 1972). The availability of micronutrients, especially Zn and Cu, is important for the optimum
growth of crops.
Zinc and copper alongside other micronutrients were first recognized as limiting factor in crop
production in Florida, United States of America during the late 1920s (Tisdale et al., 1975). The role of both zinc
and copper in plants are associated with the functioning of a number of enzymes. Zinc promotes growth
hormones, seed production and starch formation. Copper is important in photosynthesis, protein and
carbohydrate metabolism as well as nitrogen fixation (Brady, 1990).
Owonobi et al. (1990) consider fadamas to be valleys of streams, rivers and lakes, which are
traditionally cropped during the dry season. It is usually a site of busy agricultural activities throughout the year
owing to its characteristic residual and underground moisture retention within the rhizosphere for most part of
the year and the understanding that they are more fertile than their upland counterparts (Mustapha et al., 2005;
Singh and Babaji, 1990). According to Davey and Johnston (1956) fadama includes only those depressions
found in the heavy clay which are filled by the overflowing of the rivers, drainage or rainfall and which retain
water and green vegetation for some time after the rest of the countryside is dry and bare. Their good water
holding capacity and proximity to water source (streams and/or underground water) for crop insurance against
drought and/or for dry season irrigation are the main factors that have lured farmer to fadama lands (Mustapha
and Loks, 2005). In the fadamas, the soils are young and highly productive due to the seasonal flooding, which
replenishes the soil with active clay fraction, organic matter and nutrient elements.
Studies on soil micronutrients status in Nigeria, in general, and in Bauchi state, in particular, have
suffered considerable neglect (Mustapha, 2003). Most of the soil fertility workers in Nigeria did center their
works on nitrogen, phosphorus and potassium (Mustapha, 2007; Sadegh-Zadeh et al., 2008; Mustapha et al.,
2011, Daar et al., 2013). It is only of recent that work started in Nigeria, and indeed West Africa, on some
micronutrients, especially magnesium and aluminum (Jayaganesh et al., 2011).
In Nigeria today, the quest for high food production in order to meet up with the food need of the ever-
increasing population has brought about the need to harness the fertility of fadama soils that were hitherto
neglected. This is evidenced in the initiation of the National Fadama Development Projects (Fadama I, Fadama
II and Fadama III projects) by the Federal Government of Nigeria. The sustainable exploitation of the fadama
lands is, however, currently hindered by the lack of site-specific information on these soils (Mustapha and Loks,
2005) thereby rendering them vulnerable to abuse and mismanagement. In order to achieve Nigeria’s goal of
food sufficiency through the agricultural transformation agenda (ATA), a proper knowledge on the physical and
Journal of Biology, Agriculture and Healthcare www.iiste.org
ISSN 2224-3208 (Paper) ISSN 2225-093X (Online)
Vol.4, No.24, 2014
148
chemical properties of fadama soils, especially of some neglected, but important, micronutrients becomes
imperative. Similarly, the continuous cultivation of fadama soils, owing to its better crop production potential
informed the likelihood that the soil may be depleted of plant micronutrient elements.
It is against this back drop that this research work seeks to ascertain the fertility of two fadama soils by
investigating the status of zinc and copper, with a view to recommending soil amendments to improve the crop
yield of the resource poor farmer in the study area.
2. Materials and Methods
2.1 The Study Area
The study was carried out between February and June, 2012 at fadama areas of Lushi and Federal Low-cost
housing estate in Bauchi metropolis, northern guinea savanna zone of Nigeria. The area is located between
longitudes 90
00' and 100
30’N and latitudes 90
30’ and 100
30’E. The climate of the area is characterized by high
temperature and seasonal rainfall with a maximum temperature of up to about 320
C and an annual mean rainfall
range of between 1000-1250mm. Mustapha et al. (2003a) had described the fadama soils of this area as Haplic
Plinthaquults.
2.2 Soil Sampling and Handling
A total of 30 composite samples were collected according to the pedogenic horizons at the two locations (Lushi
and Federal Low-cost fadama areas) and kept in labeled polythene bags for easy identification. The collected
samples were air-dried in the laboratory until a constant weight was obtained. The samples were then ground
using porcelain pestle and mortar and sieved through a 2mm stainless steel sieve. The fine ground soil samples,
collected in separate polythene bags, were used for analyses at the Soil Science Laboratory of the Abubakar
Tafawa Balewa University, Bauchi.
2.3 Laboratory Analyses
The processed soil fractions were subjected to laboratory analyses according to the procedure outline by Page et
al. (1982). Particle size distribution and micro aggregate stability, which involved the determination of the
amounts of silt and clay in calgo-dispersed as well as water-dispersed samples using the Bouyoucos hydrometer
method of particle size analyses, was done according to the procedure described by Gee and Or (2002). Soil pH
was determined in water at a 1:1soil to water ratio using glass electrode pH meter. Organic carbon was
determined using the wet oxidation method (Walkley and Black, 1934). Micro-Kjeldhal digestion method (Juo,
1979) was used to determine total N and available P was extracted by sodium bicarbonate solution (Olsen and
Summers, 1982). Exchangeable bases (Ca, Mg, K and Na) were extracted in 1NNH4AC (1 normal ammonium
acetate) and Ca and Mg in the extracts were determined using Atomic Absorption Spectrophotometer while K
and Na were determined using flame photometer (Thomas, 1982). The CEC was determined by saturating the
soil with 1NNH4AC solution, and all the cations displaced into the soil solution were summed up. The available
Zn and Cu were extracted using 0.1 MHCL solution and the elements in the soil solution were determined by
atomic Absorption Spectrophotometer.
2.4 Data Analyses
The data obtained were analyzed using GenStat Discovery edition 4.2. Significantly different means were
separated using the least significant difference (LSD). Simple descriptive statistics including mean and range
were also used.
3. Results and Discussion
Particle size distribution and organic matter content of the soil at the study area, Lushi and Federal Low-cost, are
presented in Table 1. The particle size distribution of the soils indicated a clay loam texture with the mean value
of sand, silt and clay content being 29.0 (range=21.5-37.5), 33.1 (range=24.8-43.2) and 33.2 (range=29.2-37.2),
respectively for Lushi soils and 22.3 (range= 19.5-26.3), 25.4 (range=15.5-37.2 ) and 52.3 (range=43.5-65.2 ), in
that order, for federal Low-cost soils. At both locations, silt content significantly (p<0.05) decreases with soil
depth. Conversely, the amount of clay increases significantly (p<0.05) down the soil profile (Table 1). Mustapha
(2007) in an earlier study of fadama soils at five locations reported the predominance of silt in most of the
surface soils and the author attributed it to annual deposition through seasonal flooding. The increase in clay
down the soil profile may be as a result of the removal of the fraction by surface run-off and also by illuviation
(Mustapha et al., 2011) which is a common phenomenon in soil in the northern guinea savanna agro-ecology
(Voncir et al., 2008). The high silt and clay contents may be due to seasonal flooding which transports and
deposits these fine soil fractions, giving these fadamas the characteristic of clay loam domination. This agrees
with Davey and Johnston (1956) who described fadamas as depressions with heavy clay.
The organic C content of the soils at the both Lushi and Fedaral Low-cost fadama soil did not differed
Journal of Biology, Agriculture and Healthcare www.iiste.org
ISSN 2224-3208 (Paper) ISSN 2225-093X (Online)
Vol.4, No.24, 2014
149
significantly (P>0.05) with soil depths (Table 1) and ranged from 2.5-3.8 (mean=3.1). The mean values of the
organic C were generally low according to the ratings of Esu (1991). Lombin (1983) and Mustapha and Nnalee
(2007) reported similar low values of organic C for soils in the guinea savanna zones of Nigeria. Otisi (1996)
reported that soils with high accumulation of Ca, Mg and Na salts have low organic matter, and invariably
organic carbon.
The chemical properties of the fadama soils at the two study sites (Table 2) showed that soil pH ranged
from 5.23-6.40 (mean= 5.36) and 4.80-6.49 (mean= 5.59) at the Lushi and Federal Low-cost fadama areas,
respectively. Though generally acidic, the pH values did not differed significantly (p>0.05) with soil depths at
both locations. The higher pH reaction (Lushi=5.23; Federal Low-cost=4.80) at the upper part of the profile (0-
15cm) at both locations may be attributed to the removal of basic cations from the surface of the soil to lower
depths and probably the use of acid-forming fertilizers such as urea (Voncir et al., 2008; Mustapha et al., 2011).
Mean values for P and Ca (Table 2) did not differed significantly (p>0.05) with soil depths at both
Lushi (P=6.45mg Kg-1
; Ca=2.26mg Kg-1
) and Federal Low-cost (P=6.61mgKg-1
; Ca=2.31mgKg-1
). According to
the ratings of Esu (1991) the P and Ca content of the soils were rated as low and medium, respectively. Mg, K,
and Na recorded mean values of 3.65cmol Kg-1
, 0.47cmol Kg-1
, and 0.28cmol Kg-1
, respectively at the Lushi
fadama soils; which were also similar to the mean values of Mg (3.36cmol Kg-1
), K (0.38cmol Kg-1
) and Na
(0.26cmol Kg-1
) obtained at the Federal Low-cost fadama soils (Table 2). These nutrient elements were rated as
high (Esu, 1991). A relatively medium to high contents of K and Mg was reported by Mustapha et al. (2011) in a
similar study.
Zinc content increased significantly (p<0.05) from the upper part of the soil (0-15cm) down the subsoil
(30-45cm) and rated as low (Appendix 1) at both Lushi fadama soils (range=0.52-2.42mg Kg-1
; mean=1.36mg
Kg-1
) and Federal Low-cost fadama soils (range=0.84-2.02mg Kg-1
; mean=1.36mg Kg-1
) (Table 2). Copper
contents of the studied soils were also low and values differed significantly with soil depth. The mean value of
Cu were 0.35 mg Kg-1
(range=0.52-0.84 mg Kg-1
) and 0.83 mg Kg-1
(range=0.50-1.28 mg Kg-1
) at Lushi and
federal Low-cost fadama soils, respectively. Fagbami, et al. (1985) reported that clay content is positively
related to Zn and Cu availability; that is, Zn and Cu are most abundant where clay is high. Macias (1973) also
linked Zn and Cu availability to exchangeable bases.
4. Conclusion
The levels of the micronutrients (Zn and Cu) in the two fadama soils investigated were low. The availability or
deficiencies of other nutrient elements in the soil are related to Zn and Cu availability in the soils under study.
Soil amendments of Zn and Cu and/or application of recommended quantities of other key nutrient elements
would enhance the availability of these micronutrients for optimum yields of crops for the resource-poor farmer
in the study area.
5. References
Bouyoucos, C.H. (1951). A recalibration of the hydrometer for making Mechanical analysis of soils. Agronomy
Journal 43:434-438
Brady, N.C. (1990). The Nature and Properties of soils (tenth edition). Macmillan Publishing campany, New
York pp. 621
Da’ar, J.W., W. Manggoel, N. A. Loks and D. Mamzing (2014). Evaluation of Some Soil Properties at Kuru-Jos.
Nigerian Journal of Crop Science, 2(1):20-25
Davey, J.T. and Johnston, H.B. (1956). The African Migratory Locust in Nigeria. Anti-locust Bulletin 22: Anti-
locust Research Centre 1, Prines gate London, S.W.7.
Esu, I. E. (1991). Detailed soil Survey of NIHORT Farm at Bunkure, Kano State, Nigeria. Institute for
Ahgricultural Research, ABU, Zaria.
Gee, G. W. and Or, D. (2002). Particle size analysis. In: Methods of soil analysis, Physical methods, Dane, JH
and Topp, GC (Eds.). ASA and SSSA Madison, WI, pp. 255-293.
Fagbami, A.A; Ajayi, S.O and Ali, E.M. (1985). Nutrient Distribution in the Basement complex soils of the
tropical, dry rainforest of southwestern Nigeria; 2 micronutrients – Zn and Cu. Soil science journal 139: 531-
537.
Juo, A. S. R. (1979). Selected methods of soil and plant analysis manual series No. 170, IITA, Ibadan, Nigeria.
Lombin, G. (1983). Evaluating the micronutrient fertility of Nigeria’s Semi-arid and savanna soils.1 Cu and Mg.
Soil science Journal 135: 135-384
Macias, F.D. (1973). Copper and Zinc status in Pasture soils of Salamanca, Spain. Soil science 115: 276-283.
Mustapha, S. (2003). Fertility and productivity constraints of the basement complex- derived ustults in Bauchi
State, Nigeria. Journal of Agricultural Technology 11:11-19.
Mustapha, S. (2007). Physico-chemical properties and Fertility Status of Some Haplic Plinthanquuits in Bauchi
Local Government Area of Bauchi State, Nigeria. International Journal of Soil Science, 2(4): 214-219.
Journal of Biology, Agriculture and Healthcare www.iiste.org
ISSN 2224-3208 (Paper) ISSN 2225-093X (Online)
Vol.4, No.24, 2014
150
Mustapha, S., Voncir, N. and Umar, S. (2011). Content and Distribution of Nitrogen Forms in Some Black
Cotton Soils in Akko LGA, Gombe State, Nigeria. International Journal of Soil Science, 6 (4): 275-281.
Mustapha, S. and Loks, N.A. (2005). Distribution of available zinc, copper, iron and manganese in the fadama
soils from two District Agro-ecological Zones in Bauchi State, Nigeria. Journal of Environmental science 9 (2)
22-28.
Otisi, E. (1996). Tropical soils and their management. Unpublished lecture notes, Federal Soil Conservation
Institute, Jos, Plateau State.
Owonobi, J.J; Abdulmunini, S. and Yajok, J.C. (1990). Farmers’ participation in irrigation and management.
Proceeding of National Workshop held at Institute for Agricultural Research (IAR) Samaru, Zaria pp3-35.
Page, A. L., Miller, H. R. and keeney, D. R. (1982). Methods of soil analysis. 2nd
Edn., American Society of
Agronomy, Medison, Wisconsin, USA.
Sadegh-Zadeh, F, Samsuri, A. W. and She-Barden B. J. (2008). Movement of Nitrogen, Phosphorus and
Potassium Fertilizers in Undisturbed Soil Columns as Affected by Soil Compaction. International J. Soil
Science, 3(3):157-163
Tisdale, S.L. and Nelson, W.L. (1975). Soil fertility and fertilizer (Third edition). Macmillan publishing Co. Inc.
U.S.A pp 694
Voncir, N. S., Mustapha, S., Tenebe, A V., Kumo, A. L. and Kushswah, S. (2008). Content and profile
distribution of extractable Zn and some physicochemical properties of soil along a toposequence at Bauchi,
northern guinea savanna of Nigeria. Int. J. Soil Sci., 3:62--68
Walkey, A. and Black, C.A. (1934). Examination of Deggaref method for determining soil organic matter and
a proposed modification of the choromic titration method. Soil science 37 (1):29-38.
Table 1: Physical Properties and Organic Matter Content of Soils at (a) Lushi Fadama and (b) Federal
Low-cost Fadama
Depth(cm) Sand Silt Clay Organic C Textural class
(a) Lushi Fadama soils
0-15 21.5 43.2 33.2 3.0 Clay loam
15-30 37.5 31.2 29.2 2.5 Clay loam
30-45 28.0 24.8 37.2 2.1 Clay loam
Grand Mean 29.0 33.1 33.2 2.5
LSD(p<0.05) ns 5.26 2.85 ns
(b) Federal Low-cost Fadama Soils
0-15 19.5 37.2 43.5 3.8 Clay loam
15-30 26.2 23.5 48.2 2.9 Clay loam
30-45 21.2 15.5 65.2 2.5 Clay
Grand Mean 22.3 25.4 52.3 3.1
LSD(p<0.05) ns 7.52 4.32 ns
Key: CL=clay loam; C =Clay; ns=not significant
Table 2: Chemical Properties of soil at (a) Lushi Fadama and (b) Federal Low-cost Fadama areas
Depth pH P Ca Mg K Na Zn Cu
(cm) (1:1)H20 (mgKg-1
) (mgKg-1
) cmolKg-1
cmolKg-1
cmolKg-1
mgKg-1
mgKg-1
Lushi Fadama Soils
0-15 5.23 7.64 2.57 3.84 0.52 0.21 0.52 0.52
15-30 5.44 5.43 2.08 3.60 0.45 0.25 1.14 0.82
30-45 6.40 6.27 2.14 3.51 0.45 0.38 2.42 1.18
Grand Mean 5.36 6.45 2.26 3.65 0.47 0.28 1.36 0.84
LSD(p<0.05) ns ns ns ns ns ns 0.51 0.35
Federal Low-cost Fadama soils
0-15 4.80 6.15 2.35 2.58 0.42 0.25 0.84 0.50
15-30 5.47 5.93 2.54 4.21 0.40 0.21 1.11 0.72
30-45 6.49 7.74 2.05 3.28 0.32 0.31 2.02 1.28
Grand Mean 5.59 6.61 2.31 3.36 0.38 0.26 1.32 0.83
LSD(p<0.05) ns ns ns ns ns ns 0.54 0.43
ns =not significant
Journal of Biology, Agriculture and Healthcare www.iiste.org
ISSN 2224-3208 (Paper) ISSN 2225-093X (Online)
Vol.4, No.24, 2014
151
Appendix 1: Ratings for soil fertility classes
Parameter Very low Low Medium High Very high Units
Zn <1.0 1.0-1.5 1.6-3.0 3.1-5.0 >5.0 Mg Kg-1
Cu <1.0 1.0-2.0 2.1-4.0 4.1-6.0 >6.0 Mg Kg-1
Fe <2.5 2.5-5.0 >5.0 mg Kg-1
Mn <1.0 1.0-2.0 2.1-3.0 3.1-5.0 >50 mg Kg-1
N <1.5 1.5-2.0 >.2.0 g Kg-1
P <10 10-20 >20 g Kg-1
K <0.15 0.15-0.30 >0.30 cmol Kg-1
Ca <2 2-5 >5 cmol Kg-1
Mg <0.3 0.3-1.0 >1.0 cmol Kg-1
Na <0.2 0.2-0.3 >0.3 cmol Kg-1
O.C. <10 10-15 >15 g Kg-1
Source: Esu (1991)
Appendix 2: Soil Reaction (pH) and CEC Ratings
Source: Black (1965)
Soil reaction (pH) Cation Exchangeable Capacity (C E C)
Extremely acid 4.5
Very strongly acid 4.6-5.0
Strongly acid 5.1-5.5
Moderately acid 5.6-6.0
Slightly acid 6.1-6.5
Neutral 6.6-7.3
Slightly Alkaline 7.4-7.8
Moderately Alkaline 7.9-8.4
Strongly Alkaline 8.5-9.0
Very strongly Alkaline > 9.0
Very low <6.0 cmol.kg-1
Low 6.0-11 cmol.kg-1
Moderate 12-25 cmol.kg-1
High 26-40 cmol.kg-1
Very High >40 cmol.kg-1
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Assessment of some micronutrient (zn and cu) status of fadama soils under cultivation in bauchi, nigeria

  • 1. Journal of Biology, Agriculture and Healthcare www.iiste.org ISSN 2224-3208 (Paper) ISSN 2225-093X (Online) Vol.4, No.24, 2014 147 Assessment of Some Micronutrient (Zn and Cu) Status of Fadama Soils under Cultivation in Bauchi, Nigeria Domchang Mamzing1 Nathan Akila Loks1 Williams Manggoel1 Selchak Boyi Gojing1 Stephen Azi Ashom2 1.Department of Agricultural Technology, College of Agriculture, PMB 001, Garkawa, Plateau State 2.Department of Animal Health and Production, College of Agriculture, PMB 001, Garkawa, Plateau State Corresponding Author: williammanggoel@ymail.com Abstract The status of Zn and Cu of two fadama soils under cultivation at Lushi and Federal Low-cost Housing Estate in Bauchi, Nigeria were determined between February and June, 2012. A total of 30 composite soil samples were collected from 0-15cm, 15-30cm and 30-45cm depths from purposively selected representative locations in the study area and analyzed using standard procedures. Particle size distribution of the soils showed clay loam texture. Soil pH was strongly acidic with mean values of 5.36 and 5.59 for Lushi and Federal Low-cost soils, respectively. Low levels of organic carbon (OC), available P, and exchangeable bases were observed. Though, soil content of Zn and Cu were low, values increased significantly (p<0.05) with soil depths at both Lushi and Federal Low-cost locations. The low mean values of these micronutrients at both Lushi (Zn=1.36mgKg-1 ; Cu=0.83mgKg-1 ) and Federal Low-cost (Zn=1.32mgKg-1 ; Cu=0.83mgKg-1 ) implied that soil amendments of Zn and Cu and/or application of appropriate quantities of key nutrient elements would enhance their availability for optimum yields of crops for the resource-poor farmer in the study area. Keywords: Micro nutrients, zinc, copper, fadama soils 1. Introduction Micronutrients, though required in small quantities, are essential for the growth and development of crops. The availability of these elements in correct amounts and proportions play a vital role in the absorption of other nutrient elements, especially nitrogen, phosphorus and potassium. Micronutrients content of soils depends upon the soil types, parent material, soil pH, organic matter, clay content, amount of exchangeable bases and phosphate (Macias, 1972). The availability of micronutrients, especially Zn and Cu, is important for the optimum growth of crops. Zinc and copper alongside other micronutrients were first recognized as limiting factor in crop production in Florida, United States of America during the late 1920s (Tisdale et al., 1975). The role of both zinc and copper in plants are associated with the functioning of a number of enzymes. Zinc promotes growth hormones, seed production and starch formation. Copper is important in photosynthesis, protein and carbohydrate metabolism as well as nitrogen fixation (Brady, 1990). Owonobi et al. (1990) consider fadamas to be valleys of streams, rivers and lakes, which are traditionally cropped during the dry season. It is usually a site of busy agricultural activities throughout the year owing to its characteristic residual and underground moisture retention within the rhizosphere for most part of the year and the understanding that they are more fertile than their upland counterparts (Mustapha et al., 2005; Singh and Babaji, 1990). According to Davey and Johnston (1956) fadama includes only those depressions found in the heavy clay which are filled by the overflowing of the rivers, drainage or rainfall and which retain water and green vegetation for some time after the rest of the countryside is dry and bare. Their good water holding capacity and proximity to water source (streams and/or underground water) for crop insurance against drought and/or for dry season irrigation are the main factors that have lured farmer to fadama lands (Mustapha and Loks, 2005). In the fadamas, the soils are young and highly productive due to the seasonal flooding, which replenishes the soil with active clay fraction, organic matter and nutrient elements. Studies on soil micronutrients status in Nigeria, in general, and in Bauchi state, in particular, have suffered considerable neglect (Mustapha, 2003). Most of the soil fertility workers in Nigeria did center their works on nitrogen, phosphorus and potassium (Mustapha, 2007; Sadegh-Zadeh et al., 2008; Mustapha et al., 2011, Daar et al., 2013). It is only of recent that work started in Nigeria, and indeed West Africa, on some micronutrients, especially magnesium and aluminum (Jayaganesh et al., 2011). In Nigeria today, the quest for high food production in order to meet up with the food need of the ever- increasing population has brought about the need to harness the fertility of fadama soils that were hitherto neglected. This is evidenced in the initiation of the National Fadama Development Projects (Fadama I, Fadama II and Fadama III projects) by the Federal Government of Nigeria. The sustainable exploitation of the fadama lands is, however, currently hindered by the lack of site-specific information on these soils (Mustapha and Loks, 2005) thereby rendering them vulnerable to abuse and mismanagement. In order to achieve Nigeria’s goal of food sufficiency through the agricultural transformation agenda (ATA), a proper knowledge on the physical and
  • 2. Journal of Biology, Agriculture and Healthcare www.iiste.org ISSN 2224-3208 (Paper) ISSN 2225-093X (Online) Vol.4, No.24, 2014 148 chemical properties of fadama soils, especially of some neglected, but important, micronutrients becomes imperative. Similarly, the continuous cultivation of fadama soils, owing to its better crop production potential informed the likelihood that the soil may be depleted of plant micronutrient elements. It is against this back drop that this research work seeks to ascertain the fertility of two fadama soils by investigating the status of zinc and copper, with a view to recommending soil amendments to improve the crop yield of the resource poor farmer in the study area. 2. Materials and Methods 2.1 The Study Area The study was carried out between February and June, 2012 at fadama areas of Lushi and Federal Low-cost housing estate in Bauchi metropolis, northern guinea savanna zone of Nigeria. The area is located between longitudes 90 00' and 100 30’N and latitudes 90 30’ and 100 30’E. The climate of the area is characterized by high temperature and seasonal rainfall with a maximum temperature of up to about 320 C and an annual mean rainfall range of between 1000-1250mm. Mustapha et al. (2003a) had described the fadama soils of this area as Haplic Plinthaquults. 2.2 Soil Sampling and Handling A total of 30 composite samples were collected according to the pedogenic horizons at the two locations (Lushi and Federal Low-cost fadama areas) and kept in labeled polythene bags for easy identification. The collected samples were air-dried in the laboratory until a constant weight was obtained. The samples were then ground using porcelain pestle and mortar and sieved through a 2mm stainless steel sieve. The fine ground soil samples, collected in separate polythene bags, were used for analyses at the Soil Science Laboratory of the Abubakar Tafawa Balewa University, Bauchi. 2.3 Laboratory Analyses The processed soil fractions were subjected to laboratory analyses according to the procedure outline by Page et al. (1982). Particle size distribution and micro aggregate stability, which involved the determination of the amounts of silt and clay in calgo-dispersed as well as water-dispersed samples using the Bouyoucos hydrometer method of particle size analyses, was done according to the procedure described by Gee and Or (2002). Soil pH was determined in water at a 1:1soil to water ratio using glass electrode pH meter. Organic carbon was determined using the wet oxidation method (Walkley and Black, 1934). Micro-Kjeldhal digestion method (Juo, 1979) was used to determine total N and available P was extracted by sodium bicarbonate solution (Olsen and Summers, 1982). Exchangeable bases (Ca, Mg, K and Na) were extracted in 1NNH4AC (1 normal ammonium acetate) and Ca and Mg in the extracts were determined using Atomic Absorption Spectrophotometer while K and Na were determined using flame photometer (Thomas, 1982). The CEC was determined by saturating the soil with 1NNH4AC solution, and all the cations displaced into the soil solution were summed up. The available Zn and Cu were extracted using 0.1 MHCL solution and the elements in the soil solution were determined by atomic Absorption Spectrophotometer. 2.4 Data Analyses The data obtained were analyzed using GenStat Discovery edition 4.2. Significantly different means were separated using the least significant difference (LSD). Simple descriptive statistics including mean and range were also used. 3. Results and Discussion Particle size distribution and organic matter content of the soil at the study area, Lushi and Federal Low-cost, are presented in Table 1. The particle size distribution of the soils indicated a clay loam texture with the mean value of sand, silt and clay content being 29.0 (range=21.5-37.5), 33.1 (range=24.8-43.2) and 33.2 (range=29.2-37.2), respectively for Lushi soils and 22.3 (range= 19.5-26.3), 25.4 (range=15.5-37.2 ) and 52.3 (range=43.5-65.2 ), in that order, for federal Low-cost soils. At both locations, silt content significantly (p<0.05) decreases with soil depth. Conversely, the amount of clay increases significantly (p<0.05) down the soil profile (Table 1). Mustapha (2007) in an earlier study of fadama soils at five locations reported the predominance of silt in most of the surface soils and the author attributed it to annual deposition through seasonal flooding. The increase in clay down the soil profile may be as a result of the removal of the fraction by surface run-off and also by illuviation (Mustapha et al., 2011) which is a common phenomenon in soil in the northern guinea savanna agro-ecology (Voncir et al., 2008). The high silt and clay contents may be due to seasonal flooding which transports and deposits these fine soil fractions, giving these fadamas the characteristic of clay loam domination. This agrees with Davey and Johnston (1956) who described fadamas as depressions with heavy clay. The organic C content of the soils at the both Lushi and Fedaral Low-cost fadama soil did not differed
  • 3. Journal of Biology, Agriculture and Healthcare www.iiste.org ISSN 2224-3208 (Paper) ISSN 2225-093X (Online) Vol.4, No.24, 2014 149 significantly (P>0.05) with soil depths (Table 1) and ranged from 2.5-3.8 (mean=3.1). The mean values of the organic C were generally low according to the ratings of Esu (1991). Lombin (1983) and Mustapha and Nnalee (2007) reported similar low values of organic C for soils in the guinea savanna zones of Nigeria. Otisi (1996) reported that soils with high accumulation of Ca, Mg and Na salts have low organic matter, and invariably organic carbon. The chemical properties of the fadama soils at the two study sites (Table 2) showed that soil pH ranged from 5.23-6.40 (mean= 5.36) and 4.80-6.49 (mean= 5.59) at the Lushi and Federal Low-cost fadama areas, respectively. Though generally acidic, the pH values did not differed significantly (p>0.05) with soil depths at both locations. The higher pH reaction (Lushi=5.23; Federal Low-cost=4.80) at the upper part of the profile (0- 15cm) at both locations may be attributed to the removal of basic cations from the surface of the soil to lower depths and probably the use of acid-forming fertilizers such as urea (Voncir et al., 2008; Mustapha et al., 2011). Mean values for P and Ca (Table 2) did not differed significantly (p>0.05) with soil depths at both Lushi (P=6.45mg Kg-1 ; Ca=2.26mg Kg-1 ) and Federal Low-cost (P=6.61mgKg-1 ; Ca=2.31mgKg-1 ). According to the ratings of Esu (1991) the P and Ca content of the soils were rated as low and medium, respectively. Mg, K, and Na recorded mean values of 3.65cmol Kg-1 , 0.47cmol Kg-1 , and 0.28cmol Kg-1 , respectively at the Lushi fadama soils; which were also similar to the mean values of Mg (3.36cmol Kg-1 ), K (0.38cmol Kg-1 ) and Na (0.26cmol Kg-1 ) obtained at the Federal Low-cost fadama soils (Table 2). These nutrient elements were rated as high (Esu, 1991). A relatively medium to high contents of K and Mg was reported by Mustapha et al. (2011) in a similar study. Zinc content increased significantly (p<0.05) from the upper part of the soil (0-15cm) down the subsoil (30-45cm) and rated as low (Appendix 1) at both Lushi fadama soils (range=0.52-2.42mg Kg-1 ; mean=1.36mg Kg-1 ) and Federal Low-cost fadama soils (range=0.84-2.02mg Kg-1 ; mean=1.36mg Kg-1 ) (Table 2). Copper contents of the studied soils were also low and values differed significantly with soil depth. The mean value of Cu were 0.35 mg Kg-1 (range=0.52-0.84 mg Kg-1 ) and 0.83 mg Kg-1 (range=0.50-1.28 mg Kg-1 ) at Lushi and federal Low-cost fadama soils, respectively. Fagbami, et al. (1985) reported that clay content is positively related to Zn and Cu availability; that is, Zn and Cu are most abundant where clay is high. Macias (1973) also linked Zn and Cu availability to exchangeable bases. 4. Conclusion The levels of the micronutrients (Zn and Cu) in the two fadama soils investigated were low. The availability or deficiencies of other nutrient elements in the soil are related to Zn and Cu availability in the soils under study. Soil amendments of Zn and Cu and/or application of recommended quantities of other key nutrient elements would enhance the availability of these micronutrients for optimum yields of crops for the resource-poor farmer in the study area. 5. References Bouyoucos, C.H. (1951). A recalibration of the hydrometer for making Mechanical analysis of soils. Agronomy Journal 43:434-438 Brady, N.C. (1990). The Nature and Properties of soils (tenth edition). Macmillan Publishing campany, New York pp. 621 Da’ar, J.W., W. Manggoel, N. A. Loks and D. Mamzing (2014). Evaluation of Some Soil Properties at Kuru-Jos. Nigerian Journal of Crop Science, 2(1):20-25 Davey, J.T. and Johnston, H.B. (1956). The African Migratory Locust in Nigeria. Anti-locust Bulletin 22: Anti- locust Research Centre 1, Prines gate London, S.W.7. Esu, I. E. (1991). Detailed soil Survey of NIHORT Farm at Bunkure, Kano State, Nigeria. Institute for Ahgricultural Research, ABU, Zaria. Gee, G. W. and Or, D. (2002). Particle size analysis. In: Methods of soil analysis, Physical methods, Dane, JH and Topp, GC (Eds.). ASA and SSSA Madison, WI, pp. 255-293. Fagbami, A.A; Ajayi, S.O and Ali, E.M. (1985). Nutrient Distribution in the Basement complex soils of the tropical, dry rainforest of southwestern Nigeria; 2 micronutrients – Zn and Cu. Soil science journal 139: 531- 537. Juo, A. S. R. (1979). Selected methods of soil and plant analysis manual series No. 170, IITA, Ibadan, Nigeria. Lombin, G. (1983). Evaluating the micronutrient fertility of Nigeria’s Semi-arid and savanna soils.1 Cu and Mg. Soil science Journal 135: 135-384 Macias, F.D. (1973). Copper and Zinc status in Pasture soils of Salamanca, Spain. Soil science 115: 276-283. Mustapha, S. (2003). Fertility and productivity constraints of the basement complex- derived ustults in Bauchi State, Nigeria. Journal of Agricultural Technology 11:11-19. Mustapha, S. (2007). Physico-chemical properties and Fertility Status of Some Haplic Plinthanquuits in Bauchi Local Government Area of Bauchi State, Nigeria. International Journal of Soil Science, 2(4): 214-219.
  • 4. Journal of Biology, Agriculture and Healthcare www.iiste.org ISSN 2224-3208 (Paper) ISSN 2225-093X (Online) Vol.4, No.24, 2014 150 Mustapha, S., Voncir, N. and Umar, S. (2011). Content and Distribution of Nitrogen Forms in Some Black Cotton Soils in Akko LGA, Gombe State, Nigeria. International Journal of Soil Science, 6 (4): 275-281. Mustapha, S. and Loks, N.A. (2005). Distribution of available zinc, copper, iron and manganese in the fadama soils from two District Agro-ecological Zones in Bauchi State, Nigeria. Journal of Environmental science 9 (2) 22-28. Otisi, E. (1996). Tropical soils and their management. Unpublished lecture notes, Federal Soil Conservation Institute, Jos, Plateau State. Owonobi, J.J; Abdulmunini, S. and Yajok, J.C. (1990). Farmers’ participation in irrigation and management. Proceeding of National Workshop held at Institute for Agricultural Research (IAR) Samaru, Zaria pp3-35. Page, A. L., Miller, H. R. and keeney, D. R. (1982). Methods of soil analysis. 2nd Edn., American Society of Agronomy, Medison, Wisconsin, USA. Sadegh-Zadeh, F, Samsuri, A. W. and She-Barden B. J. (2008). Movement of Nitrogen, Phosphorus and Potassium Fertilizers in Undisturbed Soil Columns as Affected by Soil Compaction. International J. Soil Science, 3(3):157-163 Tisdale, S.L. and Nelson, W.L. (1975). Soil fertility and fertilizer (Third edition). Macmillan publishing Co. Inc. U.S.A pp 694 Voncir, N. S., Mustapha, S., Tenebe, A V., Kumo, A. L. and Kushswah, S. (2008). Content and profile distribution of extractable Zn and some physicochemical properties of soil along a toposequence at Bauchi, northern guinea savanna of Nigeria. Int. J. Soil Sci., 3:62--68 Walkey, A. and Black, C.A. (1934). Examination of Deggaref method for determining soil organic matter and a proposed modification of the choromic titration method. Soil science 37 (1):29-38. Table 1: Physical Properties and Organic Matter Content of Soils at (a) Lushi Fadama and (b) Federal Low-cost Fadama Depth(cm) Sand Silt Clay Organic C Textural class (a) Lushi Fadama soils 0-15 21.5 43.2 33.2 3.0 Clay loam 15-30 37.5 31.2 29.2 2.5 Clay loam 30-45 28.0 24.8 37.2 2.1 Clay loam Grand Mean 29.0 33.1 33.2 2.5 LSD(p<0.05) ns 5.26 2.85 ns (b) Federal Low-cost Fadama Soils 0-15 19.5 37.2 43.5 3.8 Clay loam 15-30 26.2 23.5 48.2 2.9 Clay loam 30-45 21.2 15.5 65.2 2.5 Clay Grand Mean 22.3 25.4 52.3 3.1 LSD(p<0.05) ns 7.52 4.32 ns Key: CL=clay loam; C =Clay; ns=not significant Table 2: Chemical Properties of soil at (a) Lushi Fadama and (b) Federal Low-cost Fadama areas Depth pH P Ca Mg K Na Zn Cu (cm) (1:1)H20 (mgKg-1 ) (mgKg-1 ) cmolKg-1 cmolKg-1 cmolKg-1 mgKg-1 mgKg-1 Lushi Fadama Soils 0-15 5.23 7.64 2.57 3.84 0.52 0.21 0.52 0.52 15-30 5.44 5.43 2.08 3.60 0.45 0.25 1.14 0.82 30-45 6.40 6.27 2.14 3.51 0.45 0.38 2.42 1.18 Grand Mean 5.36 6.45 2.26 3.65 0.47 0.28 1.36 0.84 LSD(p<0.05) ns ns ns ns ns ns 0.51 0.35 Federal Low-cost Fadama soils 0-15 4.80 6.15 2.35 2.58 0.42 0.25 0.84 0.50 15-30 5.47 5.93 2.54 4.21 0.40 0.21 1.11 0.72 30-45 6.49 7.74 2.05 3.28 0.32 0.31 2.02 1.28 Grand Mean 5.59 6.61 2.31 3.36 0.38 0.26 1.32 0.83 LSD(p<0.05) ns ns ns ns ns ns 0.54 0.43 ns =not significant
  • 5. Journal of Biology, Agriculture and Healthcare www.iiste.org ISSN 2224-3208 (Paper) ISSN 2225-093X (Online) Vol.4, No.24, 2014 151 Appendix 1: Ratings for soil fertility classes Parameter Very low Low Medium High Very high Units Zn <1.0 1.0-1.5 1.6-3.0 3.1-5.0 >5.0 Mg Kg-1 Cu <1.0 1.0-2.0 2.1-4.0 4.1-6.0 >6.0 Mg Kg-1 Fe <2.5 2.5-5.0 >5.0 mg Kg-1 Mn <1.0 1.0-2.0 2.1-3.0 3.1-5.0 >50 mg Kg-1 N <1.5 1.5-2.0 >.2.0 g Kg-1 P <10 10-20 >20 g Kg-1 K <0.15 0.15-0.30 >0.30 cmol Kg-1 Ca <2 2-5 >5 cmol Kg-1 Mg <0.3 0.3-1.0 >1.0 cmol Kg-1 Na <0.2 0.2-0.3 >0.3 cmol Kg-1 O.C. <10 10-15 >15 g Kg-1 Source: Esu (1991) Appendix 2: Soil Reaction (pH) and CEC Ratings Source: Black (1965) Soil reaction (pH) Cation Exchangeable Capacity (C E C) Extremely acid 4.5 Very strongly acid 4.6-5.0 Strongly acid 5.1-5.5 Moderately acid 5.6-6.0 Slightly acid 6.1-6.5 Neutral 6.6-7.3 Slightly Alkaline 7.4-7.8 Moderately Alkaline 7.9-8.4 Strongly Alkaline 8.5-9.0 Very strongly Alkaline > 9.0 Very low <6.0 cmol.kg-1 Low 6.0-11 cmol.kg-1 Moderate 12-25 cmol.kg-1 High 26-40 cmol.kg-1 Very High >40 cmol.kg-1
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