Research Article - (2014) Volume 0, Issue 0
Two greenhouse pot experiments (clayey and sandy soil) were conducted in order to evaluate the effects of solarization (covering the soil with transparent plastic sheets), inoculation with sulfur oxidizing bacteria SOB (isolated Thiobacillus), addition of filter mud cake FMC (one of the sugar industry wastes, Nagaa Hammady Sugar Factory, Egypt) as a source of organic matter and elemental sulfur on some sand and clay soil properties. In both soils, the temperature of solarized soil was always higher than the nonsolarized one with an average of 6°C at 8:00 a.m. and 14°C at 4:00 p.m. which resulted in a reduction in organic matter percentage (OM%). Both FMC and S addition had great effects on increasing soil total soluble salts compared to the increase that resulted from either solarization or SOB inoculation. The effect of elemental sulfur addition on decreasing soil pH was higher than the other treatments in clay soil, while FMC addition was the most effective treatment in sandy soil. The highest increase in available S was always found when soils were treated with elemental sulfur. Each of the treatments increased the available P in both soils; however the most effective treatment was FMC addition. Soluble Ca+2+Mg+2 and K+ were always increased due to each of the treatments. The highest increase in soluble Na+ was due to increasing soil temperature by solarization compared to the other treatments.
Keywords: Soil solarization, Sulphur oxidizing bacteria, Soil properties, Greenhouse experiments
The term ‘soil solarization’ or simply ‘solarization’ refers to the solar heating of moist soil by covering it with clear plastic sheets during periods of high solar radiation. Soil solarization induced changes in soil physical and chemical properties, such as soil structure [1,2], water potential , soil pH and EC . Solarization speeds up the breakdown of organic material in the soil resulting in release of soluble nutrients, such as calcium (Ca+2), magnesium (Mg+2), potassium (K+), and fulvic acid, making them more available to plants .
The main reasons for assigning thiobacilli as the dominate role in sulfur oxidation process in soils are: Chemolithotrophic sulfur oxidizing bacteria will oxidize reduced forms of sulfur since this is the only or preferred way of obtaining energy . Sulfur oxidation occurred more rapidly when inoculated sulfur used . However, the oxidation of reduced sulfur in soils usually regarded as a microbial process, although some non-biological oxidation of the elemental does occur . Sulfur oxidation is in fact, a chemical process, where tetrathionate accumulate at 45°C in a fertile loam soil, a result suggesting that thermophilic or abiotic oxidation of elemental sulfur to S4O6 was occurring .
The most important factors governing the rate of sulfur oxidation are temperature and water potential , variation in particles size , manufacturing processes and additives , soil fertility .
Sulfur oxidation and nutrient availability may increase with the addition of organic matter to sulfur amended soils that contains low amount of organic matter . Soil pH decreased from 8.1 to 6.7 by the application of WS 90 (wetable S) at a rate of 1000 Kg S h-1 compared with the control . Sulfur application considerably increased the EC and the soluble sulfate in calcareous soils with little differences between different rates of application  showed that. In some calcareous soil, S-application increased the chemically available P from native soil apatite or added rock phosphate , whereas in others it increased available P only when P-fertilizer was added to the soil but soil P was not affected . Our experiment was achieved to indicate the changes of the some soil properties as a result of solarization and/or inoculation with sulfur oxidizing bacteria along with sulfur and filter mud cake addition.
Two greenhouse experiments (clayey soil and sandy soil) were conducted at Soils and Water Department in black polyethylene bags 25-30 cm high, 20 cm diameter filled with 5 kg soil. The soil was irrigated and lifted for 48 hours to reach field capacity then, covered by colorless transparent polyethylene sheets. The soil was kept moist near field capacity across the experiment and water was added as the soil needed. Soil temperature was measured daily at 8:00 a.m. and 4.00 p.m. at 8 cm depth in nonmulched and mulched soils using soil thermometers. Eight weeks after the termination of solarization period the soil samples were taken with 2.5 cm diameter soil tube, air-dried and stored in plastic bags for chemical analysis .
Isolation of Thiobcillus strain
The isolate used in the present study is Thiobacillus spp. The Thiobacillus strain was isolated from composite sample of clayey soil of Assiut Experimental Farm which cultivated with faba bean plants. Starkey’s medium was used for the isolation and subsequent cultivation have the following composition NH4Cl 0.2 g, KH2PO4 0.4 g, MgCl2 0.1 g, FeCl2 trace, NaHCO3, 1.0 g and Na2S2O3 5.0 g dissolved in 1 L distil water . The medium was sterilized at 15 pounds pressure for fifteen minutes, the thiosulfate and carbonate were sterilized, separately, and then they were added by means of sterile pipettes. The initial reaction of this medium was about pH=8.6 to 9.6. Ten grams of soil were added to 200 ml of the sterilized liquid medium in a 250 ml Erlenmeyer flask and shaked on rotary shaker for 1 hr then incubated at 30-34°C for 15 days. One ml aliquots of the suspension was spread on the surface of the Starkey’s solid agar medium in Petri plates and the plates were incubated at 30-34°C for 10 days. After incubation, the developing Thiobacillus colonies were repeatedly purified by single colony isolation and the purity of the selected isolate was then tested microscopically before studying their characteristics.
Microscopic examination of the isolate grown on Starkey’s broth and agar media at age of 24 hrs and 5 day old were made for the determination of cell morphology (gram reaction dimension and motility). Also, colony characteristics (size, form, shape, surface, elevation, consistency, color and edge) were examined on the strain. The composition of broth Starkey’s medium, routinely used for growing and testing morphological and physiological characteristics of the isolate e.g., diverse growth temperature requirements of this isolate, determine the optimum growth temperature, capability of use organic substrate (yeast, glucose) and denitrification as follows:
Growth temperature requirements and determining the optimum temperature of Thibacillus spp. isolate: Five sterilized tubs (contained 9 ml of Starkey’s liquid medium inoculated with 1 ml of 5 day old isolated culture) were used in this test. The tubes were incubated at 4, 25, 30, 34, 45 and 50°C. After 5-days the positive tubes were counted .
Using (glucose and yeast extract) by isolated Thiobacillus: Starkey’s liquid medium used for this test and modified by adding D-Glucose or Yeast Extract at concentration of 5 g/L. The glucose and yeast extract prepared at this concentration and sterilized separately then, added by sterilized pipettes. Five sterilized tubs (contained 9 ml of Starkey’s glucose or Yeast Extract liquid medium) was inoculated with 1 ml of 5 days old culture of the isolated Thiobacillus, and the tubes were incubated for 5 days at 34°C, then the positive tubes were counted .
Growth curve characteristics: A growth curve was made for Thiobcillus isolate grown on a sterilized 200 ml of Starkey liquid medium dispensed in a 250 ml capacity Erlenmeyer flask (five replicate used with the same preparation medium). The medium was inoculated with 2 ml of 5 days-old culture of the strain, and the inoculated flasks were incubated for 5 days at 30-34°C. 10 ml samples of the developing cultures were taken periodically for optical density readings. The optical density was measured at wavelength 600 nm using Spectronic 20, Bauch and Lomb colorimeter .
The experimental design was factorial experiment with four factors arranged as split plots on the basis of Randomized Complete Block Design with four replications. Two levels of solarization (solarization and nonsolarization) were allocated to the main plots, and two levels of filter mud cake (with 2% filter mud cake and without filter mud cake) were assigned as subplots, two level of elemental sulfur (with 1 ton/ feddan. elemental sulfur and without elemental sulfur) were assigned as sub-subplots, and two levels of inoculation with sulfur-oxidizing bacteria (with inoculation and without inoculation) were assigned as sub-sub-subplots. Bacterial inoculums were prepared as Starkey’s liquid inoculums contained 109 viable cells/ml, determined on plates of Starke’s agar medium). Supper phosphate fertilizer was added to the hole unites of all the experiments at a rate of 1 ton/feddan in pots and laboratory experiments and 500 kg/feddan at field experiment.
The clay soil had a clayey texture (48, 29 and 23% clay, silt and sand) with 2.5% CaCO3, 1.3 dS m-1 EC (1:1), 7.6 pH (1:1 suspension) and 1. 3% OM. Whereas the sandy soil had a sandy texture (3, 8 and 89% clay, silt and sand, respectively) with 15.2% CaCO3 , 1.7 dS m-1 EC (1:1), 8.3 pH (1:1 suspension) and 0.5% OM. The used Filter Mud Cake (FMC) contained 70.74% organic matter, pH (1:10 suspension) 6.75, EC (at 25°C and 1:10 extract) 4.00 ds/m, total phosphorus (P2O5) 1.78 %, total potassium (K2O) 0.47 %, total sodium (Na2O) 0.16 %, total calcium (CaO) 0.94 %, total magnesium (MgO) 0.12 %, total sulfur (S) 2.95 %, total Fe 169.6 ppm, total Mn 297.0 ppm, total Zn 259.3 ppm and total Cu 196.9 ppm.
Total soluble salts were measured in 1:1 soil extracts by the electric conductivity method (EC) . Calcium and magnesium were titrated by versene , while sodium and potassium were measured by flamephotometere . Organic matter content was determined using Walkely-Black method, following . Soil pH was measured in a 1:1 (soil:water) suspensions using a glass electrode . Available Phosphorus was determined calorimetrically using the chlorostanous phosphomolybdic acid method according to . Available sulfur in soil samples was extracted using 500 ppm P of KH2PO4. Also, sulfur was determined in soil extracts and FMC digests by turbidity method. Soil texture was carried out using the pipette method .
Morphological, cultural characteristics and growth curve of isolated Thiobacillus strain:
Results of the tested morphological and cultural characteristics of Thiobacillus isolated strain show that cells shape were small, gramnegative, single rods, 0.5-4.0 μm in length and 0.5-1 in diameter, produce no spores and non-motile. Tables 1 and 2, respectively, indicate some cultural characteristics and the physiological characteristic determined for the isolated Thiobacillus strain in comparison to known Thiobacillus species.
|Colony characteristic||Thiosulfate medium+glucose||Thiosulfate medium|
Table 1: Cultural characteristic of isolated Thiobacillus strain on Thiosulfate medium with or without glucose.
|Formation of surface pellicle of sulfur particle on thiosulfate medium||+||+||-||+||+|
|Growth as chemolithotroph||-||-||-||-||+|
|Anaerobic growth and denitrification with thiosulfate||-||-||-||+||-|
|Growth on nutrient agar||+||+||+||-||-|
|Growth on thiosulfate agar||+||+||+||+||+|
|Mixotrophic growth with thiosulfate +glucose||+||+||+||+||-|
|Mixotrophic growth with thiosulfate + yeast extract||+||+||-||+||-|
|Autotrophic growth with sulfur||-||-||-||+||+|
|Final pH when grown on thiosulfate medium||5||5.0-5.5||5.8 -6.5||2.5-3.5||3.5-4.0|
|Proposed species||Thiobacillus novellus|
Table 2: Physiological Characteristic determined the isolated Thiobacillus strain in comparison to known Thiobacillus species (Bergy's 1989).
Cultural characteristics of the isolate Thiobacillus strain indicate that on agar thiosulfate+glucose medium the isolate produce circular, convex, yellow and viscoid colonies 1-3 mm in diameter with entire edge. Whereas, in the thiosulfate agar medium without glucose the colonies color was white and its size was 0.5-0.7 mm in diameter but with the same other previous characteristics (in the thiosulfate+glucose agar medium) (Table 1).
The physiological characteristics of the isolate Thiobacillus strain in comparison to known Thiobacillus species according to [24,25] indicate that there are four speices of Thiobacillus are too closely to our isolate. These speices are T. thioparus, T. dilicatus, T. versutus, T. novellus.
T. thioparus is strictly chemolithotroph and autotrophic bacteria. The lowest pH produced aerobically in thiosulfate medium is 3.5-4.0. T. delicatus can grow anaerobically and the lowest pH produce in thiosulfate medium is 2.5-3.5. T. versutus had ability to motile by means of polar flagella and do not form surface pellicle of sulfur particles. The lowest pH produced in thiosulfate medium is 5.8-6.5. T. novellus can grow mixotrophically on thiosulfate+glucose medium, it is facultative chemolithotrophic bacteria, the final pH when grown on thiosulfate medium is 5.0-5.5, cannot grown anaerobically, nonmotile and it can form a pellicle of sulfur particles on thiosulfate medium. Though, according to these physiological characteristics we can say that the proposal spices of the present isolate is T. novellus where the present isolate have the same characteristics of Thiobacillus novellus (Table 2).
The growth curve, drawn for Thiobacillus isolated strain in Starkey’s liquid medium is shown in Figure 1. Optical density was measured, by Spectrophotometer where the turbidity is related to both the cell numbers and the sulfur particles that produce with the growth of bacteria. Therefore, both the numbers of cells and the amount of sulfur particles could be used as a function for growth of bacteria. A lag phase of 24 hrs was recorded for the isolated strain, after which cell numbers increased exponentially with the time. As indicated from the measurement of optical density of Starkey’s liquid media, the maximum total growth for the strains occurred after 104 hrs from inoculation.
Effect of solarization on soil temperature
Curves in Figure 2 show that the weekly mean of temperature in both covered soils were generally greater than those in uncovered soils with an average of 6 and 14ºC at 8:00 a.m. and 4:00 p.m., respectively, overall the experimental period. After the fifth week, which always recorded the lowest temperatures, gradual increase in the temperature was recorded in all cases. The temperature was fluctuating due to the fluctuation of the ambient air temperature. These finding are in accordance with those reported by [24,25].
Effect of solarization, FMC and S application, and inoculation with sulfur-oxidizing bacteria on some soil properties
Main effect: Data in Tables 3 and 4 summarize the main effects of solarization, application of Filter Mud Cake (FMC), elemental sulfur (S) and inoculation with Sulfur-Oxidizing Bacteria (SOB) on some properties of clay and sandy soils, respectively. Data show the noticeable significant effects of solarization, S and FMC addition on most of the discussed soil parameters. Data indicate that solarization of clay soil caused a highly significant reduction in soil organic matter percentage by about 23% and 30% in clay and sandy soils, respectively, compared to that of nonsolarized treatments. This was due to the increase of soil temperature which was higher in sandy soil than in clay soil and resulted in rapid decomposition of organic matter. The most obvious result was the significant increase in soil organic matter content by about 73% (from 1.21% to 2.09%) and 213% (from 0.3% to 0.94%) in clay (Table 3) and sandy soil (Table 4), respectively, received FMC over the untreated soil. While the addition of sulfur decreased OM content in sandy soil by 10.6%, it had no effect in clay soil. The inoculation with SOB almost had no effect on soil OM decomposition in both soils.
|Treatment||OM (%)||EC (ds/cm)||pH||Available S (ppm)||Available P (ppm)||Soluble cations (meq/100g soil)|
FMC=Filter Mud Cake, S=granuled elemental sulfur, Ino=inoculation with Sulfur-Oxidizing Bacteria (SOB), EC=ds/m at 25°C 1:1 soil extract, pH=1:1 soil suspension, *=significant (P<0.05) ** =high significant (p<0.01).
Table 3: Main effects of solarization, FMC and S addition, and inoculation with SOB on some properties of clay soil.
|Treatment||OM (%)||EC (ds/cm)||pH (1:1)||Available S (ppm)||Available P (ppm)||Soluble cations (meq/100g soil)|
Table 4: Main effects of solarization, FMC and S application, and inoculation with SOB on some properties of sandy soil. FMC=Filter Mud Cake, S=granuled elemental sulfur, Ino=inoculation with sulfur-oxidizing bacteria (SOB), EC=ds/m at 25°C 1:1 soil extract, pH=1:1 soil suspension, *=significant (P<0.05) **=high significant (p<0.01).
Data also indicate that solarization, S and FMC addition significantly increased the EC in both soils. The increase of EC in clay soil was 16, 55 and 33% while in sandy soil it was 20, 29 and 45% for solarization, S and FMC treatments over the untreated soil, respectively.
Soil pH was significantly decreased by all the discussed treatments and in both soils as appear in Tables 3 and 4. All treatments resulted in a highly significant increase in extractable S having the highest increase in soil treated with elemental S (75% and 78% increase in clay and sandy soil, respectively, compared to the untreated soil). While solarization, FMC and SOB increased the soil S by 24, 45 and 24% in clay soil and 39, 60 and 30% in sandy soil, respectively, compared with the untreated soils.
Phosphorus availability was significantly increased by all treatments. The most effective treatment was FMC which increased available P to reach 95.86 and 81.61 ppm with an increase of 49 and 72% in clay and sandy soils, respectively. Application of sulfur and inoculation with S-oxidizing bacteria caused a noticeable effect on NaHCO3-extractable phosphorus but the amount of available P in these treatments were less than the amount found with FMC and solarization treatments in both soils. Soluble Ca+2 + Mg+2 were significantly increased by solarization, FMC and S addition in both soils as shown in Tables 3 and 4 where it reached 22.51 meq/100 g soil with S addition to clay soil and 6.48 meq/100 g with FMC addition to sandy soil. While the inoculation with SOB had no significant effects in both soils. Increases in soluble mineral nutrients including NH4, NO3, Phosphorus, K+, Ca+2, Mg+2, Mn+2, Fe+3, Cl- and Cu+2 have been detected in solarized soils in several studies  although sometimes inconsistently [27-29], especially for the minor elements [4,30].
Soil solarization was the most effective treatment in increasing soluble Na+ in both soils, where it reached 2.01 and 5.05 meq/100 g in clay and sandy soils, respectively. Soluble K+ was significantly increased in both soils under all treatments except SOB inoculation with almost the same value.
Clay soil: The interaction effects of solarization, application of FMC and elemental sulfur, and inculcation with SOB on some clay soil properties is shown in Tables 5 and 6. Although the application of FMC to solarized soil caused a significant effect on increasing soil organic matter percentage up to 1.76%, the increase of OM percentage was much higher by 63% in the nonsolarized soil received the same FMC rate Table 5. Which indicate that solarization decreases the effect of OM addition. Though, solarized soil contained higher EC than the nonsolarized ones, the addition of FMC to any of the soils resulted in more increase in the EC. Which lead to the result that the highest EC value was found when solarization was combined with FMC addition to the soil. Soil pH was significantly decreased as a result of the interaction between solarization and addition of FMC compared with the unsolarized soil without FMC addition. Available sulfates and phosphate as well as soluble Ca+2+Mg+2 in the soil recorded the highest values in solarized soil amended with FMC.
|Treatment||OM (%)||EC (ds/cm)||pH 1:1||Available S (ppm)||Available P (ppm)||Soluble cations (meq/100g soil)|
Table 5: The interaction effects of solarization, FMC and S addition, and inoculation with SOB on some soil properties, clay soil. FMC=filter mud cake, S=granuled elemental sulfur, Ino=inoculation with sulfur-oxidizing bacteria (SOB), EC=ds/m at 25°C 1:1 soil extract, pH=1:1 soil suspension.
|Treatment||OM (%)||EC (ds/cm)||pH 1:1||Available S (ppm)||Available P (ppm)||Solable cations (meq/100g soil)|
Table 6: The interaction effects of application of FMC, elemental sulfur, and inoculation with SOB on some properties of clay soil. FMC=filter mud cake, S=granuled elemental sulfur, Ino=inoculation with sulfur-oxidizing bacteria (SOB), EC=ds/m at 25°C 1:1 soil extract, pH=1:1 soil suspension.
Solarized soil received elemental sulfur contained less O.M in comparison with nonsolarized soil treated with elemental sulfur, while it contained more OM when compared with solarized soil without S addition. Mulching soil surface with clear plastic sheets resulted in significant increase in EC, available sulfates, available phosphates and soluble cations (Ca+2+Mg+2, NA+ and K+) in soil treated with elemental sulfur compared with the soils unsolarized or solarized. Which means that solarization enhanced the effect of S on decreasing the pH and thus increasing the soluble and extractable nutrients.
Addition of FMC to the soil received elemental sulfur led to great increase in soil EC, available sulfates, phosphates, and soluble Ca+2 +Mg+2 compared to soil received no FMC with or without sulfur addition (Table 6). The addition of S with or without FMC also increased these values. These facts lead to the enhancement effect of both FMC and S on each other when added together. On the other hand, OM increased by the addition of FMC but not S addition, which led to no significant effect of S on soils with or without FMC addition. The same effect was found in the soils treated with or without FMC and SOB. These results are in agreement with those reported by [31,32].
As in all S treatments, pH always decrease with the addition of S, and this decrease become even more with the addition of FMC. The same effect on pH values were found with SOB treatments combined with either FMC or S treatments (Table 6). Inoculation with SOB, ether with FMC or S treatments, had significant effect on increasing of S, P, Na+ content and accordingly EC too. This is because of the effect of these bacteria on oxidizing S in soil, which causes the increase of EC. That effect of SOB was enhanced by the application of either FMC or S. On the other hand, the increase in OM, Ca+2+Mg+2 and K+ content were mainly referred to the addition of FMC and not SOB. While S addition accompanied with SOB resulted in a significant increase in Ca+2+Mg+2 and K+ content.
Sandy soil: Data in Table 7 represent the interaction effects of solarization accompanied with applications of either FMC or elemental sulfur or inoculation with SOB on some properties of sandy soil in pot experiment. Solarization of soil amended with FMC for 8 weeks resulted in significant reduction in soil organic matter content compared with the nonsolarized soil. The same treatment exhibited the highest significant increase in EC values and the lowest value of pH, in comparison with all other treatments. This may be due to the fact that solarization of soil was accompanied with the acceleration of organic matter decomposition which resulted in release of organic acids which in turn reduce soil pH (or increase soil acidity) and increases the solubility of salts.
|Treatment||OM (%)||EC (ds/cm)||pH||Available S (ppm)||Available P (ppm)||Soluble cation (meq/100g soil)|
Table 7: The interaction effects of solarization, FMC and S application, and inoculation with SOB on some properties of sandy soil. FMC=Filter Mud Cake, S=granuled elemental sulfur, Ino=inoculation with sulfur-oxidizing bacteria (SOB), EC=ds/m at 25°C 1:1 soil extract, pH=1:1 soil suspension.
Data in Table 7 also indicate that both extractable sulfates and soluble cation were increased significantly by solarization of soil with and without FMC treatments. The increase was also found with FMC treatment with or without solarization except for NA+ which decreased, but not significantly, with the addition of FMC. Solarization of soil without FMC treatment caused obvious increase in extractable P, the same effect occurred due to the addition of FMC either with or without solarization. However, solarizing the soil treated with FMC decreased the amount of extractable P, which matches the percentage of OM .
Solarization of soil always had the same significant effect on decreasing organic matter and pH while increasing EC, S, P and soluble cations when it was combined with either S or SOB treatments. While S addition had highly significant effect on decreasing the pH and on increasing the EC, extractable S, extractable P and soluble cations either with or without solarization. On the other hand, SOB had significant effect on increasing extractable S, P and accordingly EC.
Data in Table 8 summarized the interaction effects of the application of FMC and elemental sulfur, and inoculation with SOB of sandy soil in pot experiment on some soil prosperities. Addition of FMC at a rate of 2% to the sandy soil amended or not amended with sulfur significantly increased OM percentage in the soil compared to those found in soil received no FMC or elemental sulfur. Similar trend was found in regard to Electrical Conductivity (EC). Addition of FMC alongside with sulfur to the soil led to obvious decrease in soil pH from 7.45 to 7.17 (Table 8), this mean that adding elemental sulfur to the soil may be the main reason of reducing soil pH rather than adding FMC. Application of FMC to sulfur amended or un-amended soil led to highly significant increases in both available sulfates and phosphate. Similarly, the concentration of Ca+2+Mg+2 and K+ in soil extract were greater in soil amended with FMC and sulfur than the un-amended one.
|Treatment||OM (%)||EC (ds/m)||PH||Available
|Soluble cation (meq/100g soil)|
Table 8: The interaction effects of application of FMC, S, and inoculation with SOB on some sandy soil properties. FMC=Filter Mud Cake, S=granuled elemental sulfur,Ino=inoculation with Sulfur-Oxidizing Bacteria (SOB), EC=ds/m at 25°C 1:1 soil extract, pH=1:1 soil suspension.
Application of FMC to inoculated or uninoculated soil increased OM percentage and EC in soil. It was noticeable that the application of FMC to inoculated soil scored the lowest value of soil pH. Both available sulfates and phosphates values were greater in soil amended with FMC and inoculated with SOB (Table 8). Soluble Ca+2+Mg+2 and K+ concentrations reached their highest values in FMC amended soil inoculated with SOB .
Though the effect of FMC addition in the presents of either S or SOB, was very clear on decreasing pH and increasing OM, EC, S, P, K+ and Ca+2+Mg+2, the effect of either S or SOB was found on increasing EC, S, P, K+, and Ca+2+Mg+2 but not on OM. Which indicate that the maximum values found for these parameters were because of the interaction effect between FMC either with S or with SOB. On the contrary, both FMC and S decreased soil pH and thus, their interaction had the highest effect on decreasing pH value to reach 7.17 while it reached 7.28 with the addition of FMC+ SOB.
The interaction between S addition and SOB inoculation resulted in significant increase of EC, S and Ca+2+Mg+2 which made the values of these parameters were the highest among the other treatments. On the other hand, the significant increase in NA+ and the decrease in pH may be attributed only to S addition and not to SOB inoculation as shown in Table 8.
Increasing the soil temperature due to solarization resulted in a reduction in OM percentage, while the addition of S had less effect and the incubation of SOB almost had no effect. Both FMC and S addition had great effects on increasing soil EC compared to the increase that resulted from either solarization or SOB inoculation. The effect of elemental sulfur addition on decreasing soil pH was higher than the other treatments in all clay experiments, while FMC addition was the most effective treatment in sandy soil experiments. Each of the treatments increased the available P in all experiments; however the most effective treatment was FMC addition. Soluble Ca+2+Mg+2 and K+ were always increasing due to each of the treatments. The highest increase in soluble NA+ was due to increasing soil temperature either by solarization or simulation compared to the other treatments .