Poultry manure and 2 feedstocks, namely rice husk and sawdust, were the materials used in the study. The Poultry manure was obtained from a battery cage house of the Animal Science Department at the Nyankpala Campus. Rice husk was obtained from the Savannah Agriculture Research Institute rice milling house, near the Campus and the sawdust was obtained from the Tamale wood market. There were two types of sawdust, namely, the single sawdust (SS) from Daniellia oliveri tree (African copaiba balsam tree) and the mixed sawdust (MS) from Daniellia oliveri and Chrysophylum albidum (white star apple tree) in a 1:1 (v/v) formulation. Compost bins were constructed as wooden boxes with dimensions of 90 cm × 90 cm × 90 cm. The inner wall of the bin was lined with a 200 µm-plastic films to preserve moisture and heat within the bins. The boxes were closed and kept in the open air during composting. The feedstocks combinations used on dry weight basis as treatments were 2 parts single sawdust: 1 part poultry manure (as 2SS), 3 parts single s sawdust: 1 part poultry manure (as 3SS), 4 parts single sawdust:1 part poultry manure (as 4SS), 2 parts mixed sawdust: 1 part poultry manure (as 2MS), 3 parts mixed sawdust: 1 part poultry manure (as 3MS), 4 parts mixed sawdust: 1 part poultry manure (as 4MS), 2 parts rice husk: 1 part poultry manure (as 2RH), 3 parts rice husk: 1 part poultry manure (as 3RH) and 4 parts rice husk: 1 part poultry manure (as 4RH). Each compost box was filled with a formulated mixture of feedstock plus poultry manure giving a total of nine compost boxes. The mixtures were watered to keep the moisture content at 60%. The mixtures were turned or aerated by scooping out mixtures and refilling so that the top part of the mixtures in box goes to the bottom of the box after turning. Aeration was done three times before the expected maturity period of eight weeks. Compost temperature was measured daily for 60 days using a Thermo-couple thermometer. The rice husk and sawdust feedstock and poultry manure were analyzed for physical and chemical properties before composting. During the composting, a total of twelve compost samples were taken from each treatment for physical and chemical quality analysis at two weekly intervals over 12 weeks. The parameters that were measured during composting included CO₂ evolution, electrical conductivity, organic carbon, total nitrogen and mineral nitrogen (NH₄-N and NO₃-N).

Total N was determined using the Kjeldahl digestion method [25]. Organic C was determined by the modified Walkley-Black Wet Oxidation method as outlined by Nelson and Sommers [26]. Organic C in compost and feedstock was determined by the Complete Oxidation procedure adapted from Heanes, [27]. Phosphate, calcium potassium and magnesium were determined by the colorimetery method by Watanabe and Olsen [28]. Electrical conductivity (EC) was determined by inserting the electrode of the EC meter into the compost sample suspension [29]. Crison Basic EC meter CM39P was used for the determination of EC. Crison Basic pH meter PH29P was used for the determination of pH. The concentrations of nutrients in compost and in soil samples (nitrate nitrogen, ammonia nitrogen) were done using UV/VIS spectrophotometer. Nitrate as nitrogen was determined by the Hydrazine Reduction Method [30]. Ammonia as ammonium nitrogen was determined by the Indophenol Blue Method [31]. Lignin and cellulose were determined following the method by Van Soest [32]. Rate of respiration (CO₂ evolution) was determined following the methods of [33]. Media moisture and temperature were determined in-situ, using a Thermo-couple thermometer and portable moisture meter respectively (Hanna instruments, Madrid Spain).

Data on quality of feedstock treatments (poultry manure, sawdust, rice husk) were analyzed using analysis of variance (ANOVA), in Gentstat version 9.2. Least significant differences (LSD) were calculated and the probability of treatment means significantly different was set at p = 0.05. Data on compost quality were analyzed by ANOVA using STATISTIX version 10 and Tukeys Honestly Significant differences were calculated at 5% level of probability (p = 0.05). Relationships between stability indices were established using correlation and regression analysis.

Poultry manure as compared to the other feedstocks, was significantly higher (p = 0.017) in N (4.37%), P (1.05%), (p = 0.044), K (4.10%); p = 0.030, Ca (4.47%); p = 0.010, Mg (3.1%); p = 0.002 and higher in density (0.5 g/cm³); p = 0.003. For the other parameters, all feedstock had similar nutrient content. The MS was highest in moisture content (12.1%); p = 0.001, total organic carbon (TOC) (45.1%); p < 0.001, cellulose (42.1%); p < 0.001 and lignin (23.7%); p = 0.040. The SS was highest in EC (8.7 mS/cm³); p = 0.001 (Table 1). The SS feedstock had the highest C:N ratio of 170 than MS feedstock (110.19) and RH feedstock (106.23).

The 2SS and 3SS maintained temperature above 40˚C (thermophilic temperature) for one week before falling below 40˚C (mesophilic). The 4SS could only maintain the temperature for four days. Turning the compost resulted in increasing the temperature to 43˚C. The highest peak temperature (51˚C) was attained in 2SS compost at 43 days and 50˚C for 4SS at 41 days. After 43 days, the

*Adopted and modified from Abubakari et al., 2017.

temperature dropped below 40˚C and close to ambient temperature of 35˚C. (Figure 1(a)).

In the mixed sawdust compost, temperature in rose to 41˚C overnight for 2MS and 4MS. Within the same period, temperature in the 3MS compost rose to 45˚C. These temperatures were maintained for three days before falling to values below 40˚C. After turning the compost at one week, the temperature fluctuated between thermophilic and mesophilic states until it fell to ambient temperature levels at day 43. Turning the compost at this stage increased temperatures to 49˚C for 3MS and 50˚C for 4MS. There was a sharp drop in temperature to ambient levels in all three mixed sawdust compost (Figure 1(b)).

In all the rice husk compost, temperatures rose above 40˚C within 24 hr. of composting. Between 3 and 8 days, the 3MS attained the highest temperature of 47˚C. At 33 days temperature in all the ratios fell to ambient levels. After the compost at 33 days, the 2SS attained peak temperature of 45˚C - 48˚C and maintained this range of temperature for 5 days (Figure 1(c)).

The CO₂ evolution was similar for all compost treatments. At the start of composting, CO₂ level ranged from 100 - 129 mg/kg/h. The CO₂ level rose to 268.5 mg/kg/h at 2^nd week of composting. At the 4^th week, CO₂ increased to 306.1 mg/kg/h and then declined to values between 84.95 and 116.47 mg/kg/h. When the compost was turned for curing at the 12^th week, the CO₂ level increased (not significant) slightly especially 4MS based compost (Figure 2).

At the start of composting, the pH of 4MS based compost (pH of 8.8), 2MS and 3MS based composts (each having pH of 8.5), were highly alkaline compared to the 2SS based compost (pH of 7.8) was slightly alkaline. At 2^nd week of composting, pH values dropped to values ranging from neutral in 3MS based compost (pH value of 7.0) to slightly acidic in 4SS based compost (pH of 6.5). There

were no significant differences in pH values between 2^nd and 6^th week of composting. At 8 - 12^th week, the 3MS and 4MS based composts had neutral pH higher than all other treatments. The 3RH, 4RH and 2MS based composts were slightly acidic, with pH (6.8) lower than all other treatments (Figure 3).

At the start of composting of the 2SS based compost had the highest EC of 3.9, significantly greater than 3SS and 4SS based composts, which had the least EC of 2.7 and 2.2, respectively (Figure 4(a)). After 2^nd week of composting, all three SS based composts had similar ECs. After 4^th week of composting however, 4SS based compost had significantly higher EC than 3SS based compost which had the lowest. Showing consistency, after 8^th week of composting, 4SS based compost continued to have the highest EC, significantly greater than those of 2SS and 3SS based composts. However, at 12^th week of composting, all three SS based composts recorded similar EC (Figure 4(a)). From the start of composting till 8^th week of composting, all the three MS based compost had similar EC. After 4^th and 8^th week of composting, the 2MS and 3MS based compost had significantly higher EC than the 4MS based compost which had EC value of 1.7 mS/cm³. However, after 8^th week of composting, all three MS based composts had similar EC values (Figure 4(b)).

At the start of composting, the 2RH based compost had EC of 3.9 significantly higher than 3RH and 4RH based composts with ECs of 2.9 and 2.8 respectively. After 2^nd and 4^th weeks of composting, the 2RH and 3RH based composts had significantly lower EC than 4RH based compost. However, at 8^th week and 12^th week of composting, all the three rice husk composts had similar EC (Figure 4(c)).

At 4^th week of composting, 4MS based compost shows the highest C:N ratio,

significantly greater than the rest of the composts, except that of 3MS based compost which was similar (Table 2). The least C:N ratio was shown by 2RH based compost. At 8^th week of composting, 4MS based compost continued to show the highest C:N ratio, significantly greater than all the other composts. The least C:N ratio was shown by 2RH based compost. However, at 12^th week of composting, 4RH based compost had the highest C:N ratio, significantly greater than the rest of the composts. The least C:N ratio was recorded by 2SS based compost. In comparison to the referenced quality standards, all the composts had attained maturity at 12^th week of composting, except 4RH based compost which had C:N ratio still above the standard (Table 2).

The 2SS based compost showed significantly highest total nitrogen content (2.46%), whereas the 4RH based compost showed the least (1.32%). The 2MS based compost had the highest carbon content (39.62%), while the 4RH base compost had the lowest carbon content (33.28%). The highest C losess occurred in 4RH compost and the least C losses occurred in 4SS. The NH₄-N level was highest in 2MS based compost (215.98 mg/kg) and lowest in 4SS based compost (23.45 mg/kg). The 2SS based compost showed the lowest C:N value (15.76) whereas the 4RH based compost had the highest C:N value of 26:23. The 2SS had the highest EC of 1.87 mS/cm³ whereas 4MS had the lowest EC value of 0.22 mS/cm3 (Table 3).

In terms of associative relationships, for single species sawdust compost, the following correlations were found; Total nitrogen (TN) and pH (r = −0.80, p <

Reference compost quality standard, C:N ratio of 15 - 25 (Sæbøa and Ferrini, 2006).

C** = losses based on initial feedstock carbon value; ***Sæbøa and Ferrini, 2006. 2SS = two parts of single species sawdust to one part poultry manure; 3SS = three parts of single species sawdust to one part poultry manure; 4SS = four parts of single species sawdust to one part poultry manure; 2MS = two parts mixed species sawdust to one part poultry manure; 3MS = three parts mixed species sawdust to one part poultry manure; 4MS = four parts mixed species sawdust to one part poultry manure; 2RH = two parts rice husk to one part poultry manure; 3RH = three parts rice husk to one part poultry manure; 4RH = four parts rice husk to one part poultry manure.

0.001, n = 40); TN and C:N (r = −0.96, p < 0.001, n = 40); TN and CO₂ (r = −0.83, p < 0.001, n = 40) and CO₂ and pH (r = −0.91, p < 0.001, n = 40).

For mixed species sawdust compost, the following correlations were found. Total N and pH (r = 0.567, p < 0.001, n = 40); TN and C:N (r = −0.94, p < 0.001, n = 40); TN and CO₂ (r = −0.73, p < 0.001, n = 40) and CO₂ and pH (r = −0.56, p < 0.001, n = 40).

For rice husk compost, TN was significantly and positively correlated with pH (r = 0.656, p < 0.001, n = 40) but negatively correlated with C:N (r = −0.880, p < 0.001, n = 40) and CO₂ (r = −0.642, p < 0.001, n = 40). The CO₂ was negatively correlated with pH (r = −0.710, p < 0.001, n = 40).

Total nitrogen was related to the C:N content of the compost depending on the base material of the compost. For single species sawdust compost, total nitrogen accounted for 93% of the variation in the C:N content of the compost in the relationship;

Y ( C / N ) = 50.099 − 14.502 X ( T N ) ;   R 2 = 0.93 ; p < 0.001 ; n = 40 , (1)

However, for mixed species sawdust compost, total nitrogen explained 87% of the variation in the C:N content of the compost in the relationship;

Y ( C / N ) = 58.455 − 19.541 X ( T N ) ; R 2 = 0.87 ; p < 0.001 ; n = 40 , (2)

Total nitrogen explained 77% of the variation in the C:N content of the rice husk compost in the relationship;

Y ( C / N ) = 47.126 − 16.795 X ( T N ) ; R 2 = 0.77 ; p < 0.001 ; n = 40 , (3)

MS feedstock was found to have higher OC and more lignin than SS feedstock and rice husk. However, the SS feedstock had the highest initial C:N compared to MS and RH. In characterizing feedstock for composting, the C:N ratio is critical as it determines the length of the thermophilic phases and also the maturity of and stability periods of the final compost. The optimum C:N ratio for matured and stabilized compost is 12:1 to 15:1 [19]. A C:N ratio less than 10:1 indicates situations of incomplete composting associated with higher levels of N manures. C:N ratio values of more than 25:1 indicate presence of raw carbonaceous materials which when applied to soil results in severe N drawdown [19]. Leconte et al. [14], characterized poultry manure and found that it had high N concentration (N = 3.7%) and low organic carbon (29%) compared to sawdust (N = 0.6, and C = 53.2%) and rice husk (N = 0.4% and C = 42.0%). Poultry manure was also found to a have high pH (8.0) and Ca (19.4%) concentration.

Leconte et al. [14], reported that, the high temperatures associated with the composting process was due largely to organic matter breakdown, increasing microbial population and activity and reducing supply of O_2. During the first 4 - 5 days, the compost pile is characterized by fermentation which results in enhanced breakdown of highly lignified carbonaceous materials. This stage is associated with significant multiplication of microorganisms. The nature of carbonaceous materials ultimately determines the length of the thermophilic phase [15]. Higher values of respiration (340 - 466 mg/kg/h) were reported at early stages of composting decreasing to 37 - 90 mg/kg/h by maturity period of compost [14]. Although increasing microbial respiration was correlated with increasing compost temperature [34], Leconte [14] found the reverse and attributed that to thermic inertia which was thought to be the result of exothermic hydrolysis.

Decreased pH may result from anaerobic conditions in compost which leads to the accumulation of organic acids such as acetic acid and propionic acid. The presence of these acids in the potting media causes the media to become toxic to seeds and seedling development [35]. Generally, the pH of a compost depends partly on the nature of the initial feedstocks. Feedstocks of higher C:N ratio are known to generate higher pH and ammonia gas during composting whiles N₂O emissions are known to be highest at low pH. Moreover, there is stabilization of pH as a result of ammonia volatilization and H⁺ release from microbial nitrification [15]. Therefore, for N mineralization to be uninhibited, the pH levels should not be less than 5 or greater than 8 [20]. In the present study, nitrogen release in sawdust was positively correlated with TN and negatively with pH [21].

Furthermore, the EC values at the end of composting for all the nine compost types were lower than the referenced compost quality standard, an indication that the composts could not be a source of toxicity to seeds or seedlings that would be planted in them. EC, a measure of soluble salts content of the compost, affects seed germination and root development and higher levels cause severe phytotoxicity [36]. If the EC is less than 0.75, the media will require nutrient supplementation. Acceptable range of EC is between 0.75 and 2.35. Consequently, in the present study, 2RH, 3RH, 3MS and 4MS composts would require nutrient supplementation since their EC values were below 0.75. Increase in EC could be due to release of mineral salts that occur during the active phase of composting [37]. Composts with EC of 5 or more needs to be applied in lower concentrations or used as mulch for established plants [23].

The quality of compost produced in this study was influenced not only by the nature of bulking materials (carbonaceous materials) but by the amount of poultry manure (N level) incorporated. The 2:1 ratio of SS to poultry manure (33% of poultry manure addition) resulted in the highest N level of 2.46% in SS based compost compared to 3:1 ratio (or 25% addition of poultry manure) with N level of 2.11% and 4:1 ratio (or 20% poultry manure addition) with 2.02% N level. In the RH based composts, the same pattern was seen in the RH based compost where higher addition of poultry manure resulted in higher N level in the matured compost. However, in the MS based composts, the reverse is the case where higher addition of compost actually resulted in lower levels of N in the final compost. In SS based composts, C losses were higher in 2SS compost where there was higher amount of poultry manure incorporated during composting and the least carbon losses occurred in 4SS composted where there was lower addition of poultry manure was used during composting. In the MS and RH based composts, carbon losses did not appear to be related to the amount of poultry manure added during composting. The quality of composts produced in the present study is comparable to composts produced elsewhere using different feedstocks [14] [38] [39] [40]. However, the SS based compost had higher (1117.81 mg/kg - 1138.6 mg/kg) than recommended levels of NO₃-N. All the C:N values found in the compost produced except 4RH, were within levels acceptable for stabilized compost (15:1 - 25:1). In the present study, correlation analysis highlighted significant relationships among the compost maturity indices. In all the different feedstock used, TN was always positively correlated with pH, but negatively correlated with C:N and CO₂. This finding was significant as it indicated that as the degradation of carbon leads to the accumulation of nitrogen, pH reaches alkaline levels. This is associated with matured compost and CO₂ values decline because of reduced microbial activity associated with maturity. The empirical relationship established between TN and C:N indicates that although TN is the dominant factor explaining variation of C:N and hence compost maturity, the extent to which TN could explain variation in CN depended on the nature of carbonaceous materials.