HOUSEHOLD SOCIO-ECONOMIC FACTORS AND SOIL FERTILITY MANAGEMENT ON MILLET FIELDS OF SOUTHWESTERN NIGER.
Soil fertility decline is a major concern in sub-Saharan Africa, particularly in Niger where agricultural activities generally depend on rainfall [1-4]. The rainfall pattern is unimodal and spread over a 3 to 4 month period (June- September). Poor fertility of the highly weathered and mostly sandy soils, where pearl millet (Pennisetum glaucum) is generally grown, combined with low input cropping, typical high rainfall variability and high temperatures lead to frequent and severe droughts which are responsible for recurrent crop failure [5-8].
Several studies have evaluated the potential of Soil Fertility Management Technologies (SFMT) to cope with the fertility problems in sandy soils . These studies have shown that the application of inorganic and organic amendments in combination with soil and water conservation measures can significantly increase crop yields, while significantly improving soil fertility [1, 10, 11, 12]. However, there is a low adoption of SFMT by the predominantly peasant farmers, practicing low input agriculture, which continuously aggravates the soil fertility problem [5, 12,13]. A variety of constraints, that explain this poor adoption, has been unveiled in several adoption studies in sub-Saharan Africa [12, 13 - 16]. Poor mineral fertilizer use or application below recommended rates in Niger has been ascribed to limited access to credit, purchasing power and knowledge [13, 17, 18]. [13, 16] attributed low uptake of new technologies in West Africa to limited productivity gain and differences in priorities between the agronomists, whose aim is to improve yields, and the Sahelian farmers who seek to reduce the risk of crop failure. In the case of crop residue management, low adoption is due to competitive domestic use for animal feed, building material and fuel. Furthermore, crop residues are required in large quantities while the practice of continuous cropping does not generate enough to be used appropriately [19 - 22]. Limited availability of manure and lack of knowledge on water and soil conservation practices are the main reasons for poor technology adoption in Western Niger . Similar reports from the eastern part of Africa indicated factors such as farmers' access to land and capital resources to be important determinants of decision to adopt Integrated SFMT or not [23, 24]. An adoption study in the Meru South District of Kenya noted farmers' ability to hire labour, age of household head, and household food security as important elements of soil fertility management .
Agricultural activities in Niger are known to be nutrient mining . In such systems, more nutrients are being exported than applied, which leads to a complete loss of soil productivity. Nutrients that are exported as harvest and crop residues from the soils should be replenished in order to alleviate this problem . To that effect, farmers traditionally use local strategies including long bush fallow, corralling, application of household and farm yard manure or application of crop residues . However, due to high demographic pressure combined with other socio-economic and cultural beliefs such as uncontrolled grazing and farm fragmentation, some of these practices have been abandoned  and are replaced by unsustainable soil management practices that expose the soil surface, remove crop residues or resort to cultivation of marginal lands. These unsustainable practices lead to further degradation of soil physical quality including complete loss of soil structure, organic matter decline, leaching losses and surface sealing which ultimately leads to excessive run-off.
There is still need for better understanding of socio-economic factors that enhance farmers' access to farm inputs and those that influence their ability to invest in fertility maintenance of their farms, for better targeting of future interventions. A long-term on-farm trial involving pilot farmers, aimed at identifying sustainability indicators and optimizing resources on soil fertility restoration, which has just been concluded and lessons learned on biophysical aspects  could be used. This could better help appreciate socio economic conditions affecting farmers SFMP. This could similarly help in devising appropriate and practicable soil management practices that can conserve soil and sustain crop production while replenishing and maintaining soil fertility. The objective of this paper was therefore to explore the influence of farmers' socio-economic conditions on soil fertility management and farm income among small-scale farmers in the study area. It was hypothesized that participation by farmer in project or farmer group activities, resource endowment and farmer SFMP are associated, and that participant farmers who are resource endowed use SFMP better than those that do not participate and are resource constrained.
Description of the study area
The current study was carried out in Karabedji (13[degrees]16' N, 2[degrees]30' E) situated at about 60 km from Niamey in the Southwestern part of Koure District (Figure 1). Koure is in the Sahel Soudan agro-ecological zone, characterized by a 3 to 4 months growing season (from July to September) and a long dry season spanning October to June. Rainfall in the area is highly variable in time and in space  with a five-year average of about 550 mm. The dominant agricultural system is subsistence crop-livestock system, in which pearl millet is grown by farmers as a sole crop, in mixed cropping with sorghum, groundnut, and cowpea and in rotation with legumes (cowpea and groundnut). The dominant soil type is classified as Arenosol  or Psammentic Paleustalfs . This soil type is characterized by coarse texture, high infiltration rate, low organic carbon content, low cation exchange and buffer capacities and low available phosphorus (P) and total nitrogen (N) contents .
Selection of respondents and sample size
The socio-economic survey was conducted between May and June 2013 to study the influence of some socio-economic factors on farmers' SFMP. General census records and key informants were used to randomly select non-demonstration participant respondents. Survey respondents included inhabitants of 5 neighboring villages namely, Seke Koira Zeno, Seke Koira Tegui, Gobriko Beri, Gobriko Zanguina and Karabedji. The farmers from Karabedji village consisted of respondents who were either or not involved in a project dealing with a long-term on-farm demonstration (demo) for evaluation of soil fertility restoration technologies (SFRT). The aim of this long-term SFRT trial, initiated in 1999 on 23 famers' fields, was to identify sustainability indicators and optimize the use of both organic and inorganic resources available to famers. The trial consisted of millet cultivation under three different rates of fertilizer micro dosing and a control treatment (no fertilizer) on the farmers' fields. The fertilizer rates were: i) control (no fertilizer), ii) 4 kg P [ha.sup.-1] as NPK 15-15-15, iii) 4 kg P [ha.sup.-1] as DAP (Diammonium phosphate) and iv) 4 kg P [ha.sup.-1] as NPK 15-15-15 + 13 kg P [ha.sup.-1] PR (Rock phosphate).
Besides 17 out of the 23 farmers involved in the long-term on-farm trial (demonstration participants), 24 other farmers from Karabedji were interviewed together with 15 farmers from each of the four neighboring villages, making a total of 101 households. Population sizes in the survey-villages were about 6000, 2000, 1500, 1800 and 1900 people for Karabedji, Seke Koira Tegui, Seke Koira Zeno, Gobriko Beri and Gobriko Zanguina respectively, according to local District office documents.
Data collection and processing
The survey was carried out using a semi-structured questionnaire with questions on individual and household information, farmers' resource endowment, SFMP and farmers' view about farming-related constraints and opportunities. The questionnaire was pretested one week before the survey. Questions on farm income and inputs seemed very sensitive to farmers in the locality, therefore farmers were asked to choose a range of income to which they belonged, as respondents hesitated during the questionnaire pretesting phase. Moreover, for comparison purposes, among respondents, the total number of animals and birds possessed by a farmer was expressed as Tropical Livestock Unit (TLU), where one TLU is equivalent to 250 kg of biomass [29, 30]. The conversion factors used were 0.7 for cattle, 0.5 for donkey, 0.10 for sheep and goat, and 0.01 for chicken and the calculation was undertaken following completion of the survey.
The total quantity of yearly-applied household manure was assessed through the number of carts of transported manure. Where farmers solicited corralling from Fulani herdsmen to settle on their farms (during the dry season) for manure, compensation in kind is given such as 100 kg bag of millet, sorghum or maize to the herder. Therefore, the equivalent value (in Fcfa) of the compensation given out by the farmer was used to estimate the cost of manure. The total household wealth (resource endowment) was estimated using the total value of animals and assets possessed as follows: cow = Fcfa 90,000, calves = Fcfa 60,000, donkey = Fcfa 40,000, sheep = Fcfa 25,000, birds = Fcfa 1,500, cart = Fcfa 100,000, radio = Fcfa 10,000, TV = Fcfa 40,000, bicycle = Fcfa 45,000, motorcycle =Fcfa 300,000 and barrow = Fcfa 35,000 [38, 39]
The survey data was analyzed using cross tabulation and logistic regression in SPSS (21st edition). The logistic regression indicates how independent variables (farmer's socioeconomic characteristics) influence the probability of the application of different SFMP (dependent variables) in the study area. Likelihood Ratio (LR) tests are used to test the null hypotheses that there is no relationship between the log of odds of the soil fertility management practices and the set of independent variables included in the models.
RESULTS AND DISCUSSION
Characteristics of participant and non-participant respondents of the demonstration
The household characteristics of demonstration participants and non-participants are presented in Table 1. Although forty-three (43 %) of demonstration non-participants and 29 % of the participants of the on-farm evaluation of SFMT, respectively, did not attend formal school, an important part of participants and non-participants of the demonstration (53 % and 39 %, respectively) did Koranic studies. There is a high proportion of non-educated farmers, showing a low level of formal education of the farming communities in the study area which could affect the dissemination of SFMT as this can interfere with the learning process through extension materials as previously reported .
The mean household size among respondents ranged between 9 to 14 dependents. Niger has one of the world's highest childbirth rates (3.7 %) and has a fecundity of about seven children per woman . However, despite the high birth rate and large household size, labour availability could be one of the main constraints to the adoption of new technologies. A local common practice in the study area is the seasonal migration to urban areas and neighboring countries. This has a direct effect on labour availability and contributes majorly to the household income and the remittance received from migrants is used to purchase farm inputs back home. The seasonal migrants furthermore do not return in time to provide help with the high labour demand for farm management operations such as planting and weeding at the beginning of the rainy season. This notwithstanding, innovative soil management technologies such as fertilizer micro-dosing technique generally requires more labour than the conventional practice.
Sixty nine percent (69%) and 55% of participant and non-participant farmers of the demonstration, respectively, were affiliates of FBO. Whereas, 70% of participant and 75% non-participant respondents had average farm income lower than Fcfa 300,000 (Table 1). Twenty nine percent (29 %) of demonstration participants had average farm income greater than Fcfa 300,000 compared to 24 % for the demonstration non-participants. The characteristics of both demonstration participants and non-participants were similar for other parameters.
All demonstration participant farmers used chemical fertilizer and 65% of them used crop residue (straw) mulch. However, more demonstration non-participant farmers use hand or hoe cultivation practice (Table 2).
Farmers' socio-economic characteristics and the application of different soil fertility management practices
Maximum likelihood estimates of parameters in the logistic regression models characterizing SFMP of demonstration participants and non-participants are presented in Table 3. The log likelihood tests showed that the estimated models, including the constant and set of explanatory variables, fit the data better compared with those containing the constant only. Therefore, there is a significant relationship between the logs of odds probability of using SFMP, and the explanatory variables included in the models. This relationship suggests that these variables contribute significantly, as a group to the explanation of SFMP of the sample farmers although several coefficients were not significant individually.
The [R.sup.2] values ranged from 40 to 84%, which also suggest that the estimated soil fertility-management models had a good explanatory power, particularly the one for the hoe cultivation method. Overall, the majority of variables had the expected signs of coefficients and those with unexpected signs were mostly statistically not significant (Table 3).
Of the independent variables, affiliation to FBO, average farm income and ownership of animal-draught cart had significant positive effects on chemical fertilizer use by farmers (Table 3). The first two variables were also found to be positively associated with the use of other special SFMP such as Zai (planting pits) and treatment of erosion-affected areas on the farm.
Moreover, participation in demonstration activities, resource endowment, average farm income, and ownership of assets such as carts, motorcycle and bicycles were significantly associated with the purchase of chemical fertilizer. However, the negative association between participation in demonstration activities and resource endowment on one hand, and the purchase of chemical fertilizer on the other was surprising.
Furthermore, average farm income was significant and positively correlated with purchase, use of chemical fertilizer and straw mulch, and other special soil fertility management works. In addition, membership of FBO, possession of animal drawn cart, average farm income and education level were positively associated with straw mulching practice. Whereas, village status, amount of hired labour, ownership of animal drawn cart and resource endowment had a significant negative relationship with hoe cultivation practice. Among other variables that showed unexpected signs of coefficients are resource endowment, which had a significant negative effect on straw mulch application, and village status found to be negatively associated with cultivation practice and use of special SFMP.
The main findings of this study are in the relationship between participation in FBO and demonstration activities, possession of cart and average farm income and SFMT in the evaluation of socioeconomic factors influencing farmers' practices.
Affiliation to FBO was found to be significantly and positively associated with SFMP such as chemical fertilizer use, application of straw mulch and practicing other special work intended to improve soil quality. This positive relationship suggests that membership in FBO has influence on farmers' capacity to manage the fertility of their farm. Indeed, participation to FBO activities would not only improve farmers' awareness of farm inputs, but also enhances their skills through better access to technical know-how, training provided by projects and extension . Farmers' associations serve as entry point for both public and other development agencies' interventions in rural areas. Moreover, FBO farmers get involved in other local initiatives that strengthen exchanges between members and thereby facilitate the passing on of information about new technologies or the availability of farm inputs among farmers. Accessibility to advisory services and farmers' perception on SFMT has been reported to impact sorghum production in Busia county of Kenya . Earlier studies in Northern Ghana reported membership of FBO among several factors affecting fertilizer technologies adoption by farmers [35, 36].
The negative association between farmers' purchase of chemical fertilizer and participation in a particular project activity and resource endowment status is surprising and may be due to the fact that mineral fertilizer loans are supplied by the project during the demonstration activities. Actually, farmers involved in on-farm demonstration activities received some quantities of fertilizer supplied by the project as loans in order to enable adequate and timely application. As for the negative association between resource endowment status of the farmer and fertilizer purchase, it clearly illustrates the key role played by other behavioral factors . Often farmers attribute their inability to purchase and use chemical fertilizer to the lack of purchasing power, which was earlier reported as a factor of fertilizer adoption . Most farmers do not purchase and keep fertilizer when they have enough cash such as after selling their crop produce. Yet, Adolwa  noted that adoption is a nuanced process, which may require non-adoption, re- testing and continuous adoption.
Average farm income and possession of animal drawn cart also positively influenced purchase and use of chemical fertilizer meaning that farmers with high average farm income and those possessing cart are more likely to purchase and use it. Fertilizer price relative to millet price was reported among the major factors determining fertilizer use in the Sahel . Farmers' resource endowment was previously reported to influence fertility status of the farm .
This study showed that farmers' socio-economic factors influence their SFMP. Affiliation to FBO was found to influence farmers' decision to purchase and apply chemical fertilizer, and their ability to use other soil fertility management practices such as straw mulch application. The results also highlighted the fact that farmers' demonstration participation and resource endowment status does not necessarily imply that they purchase and use mineral fertilizer. Yet, high average farm income of the farmer and possession of assets such as animal drawn cart were found to be positively related with SFMP tested. To enhance farmers' access and use of agricultural inputs such as fertilizer, policy efforts should not only focus on timely supply, but also on organization and awareness creation particularly conditions that will enable farmers to acquire fertilizer and keep it for future use, as they may not have cash during the planting season when they mostly purchase food. Further studies could also look at the benefit of such purchase ahead of time by farmers on their fertilizer use.
We would like to thank the Alliance for Green Revolution in Africa (AGRA) for sponsoring the project through its Soil Health Program (2009 SHP 028). We notably thank Abdou Adamou, Zakari Seydou, Harouna Mounkaila and Hassane Ide for their advice and assistance during the field work.
(1.) Bationo A and BS Waswa New Challenges and Opportunities for integrated soil fertility management in Africa. In: Bationo A, Waswa BS, Okeyo JM, Kihara JM F Maina (Eds) Innovations as key to Green revolution. 2011; (1): 3-15.
(2.) Sivakumar MVK Climate change and implications for agriculture in Niger. Climate Change. 1992; (20): 297-312.
(3.) Sivakumar MVK, Maidoukia A and RD Stern Agro meteorology of West Africa, Niger. ICRISAT Information Bulletin No. 5, ICRISAT, Patancheru, Andra Pradesh, India, 1993.
(4.) Greaf F and J Haigis Spatial and temporal variability in the Sahel and its effects on farmer's management strategies. Journal of Arid Environments. 2001; (48): 221-231.
(5.) Pender J, Abdoulaye T, Ndjeunga J, Gerard B and E Kato Impacts of inventory credits, input supply shops, and fertilizer Micro-dosing in the Dry lands of Niger. International Food Policy Research Institute, Environment and Production Technology Division. IFFRI, Discussion paper Series No 763, 2008.
(6.) Heano J and CA Baanante Agricultural production and soil nutrient mining in Africa: implications for resources conservation and policy development. International Fertilizer Development Center (IFDC), Muscle Shoals, Alabama, USA, 2006.
(7.) De Ridder N, Breman H, van Keulen H and T Jan Stomph Revisiting a "cure against land hunger": soil fertility management and farming systems dynamics in the West African Sahel. Agricultural Systems. 2004; (80): 109-131.
(8.) Samake O, Smaling EMA, Kropff MJ, Stomph TJ and A Kodio Effects of cultivation practices on spatial variation of soil fertility and millet yields in the Sahel of Mali. Agriculture, Ecosystem and Environment. 2005; (109): 335-345.
(9.) Bationo A, Kihara J, Waswa B, Ouattara B and B Vanlauwe Technologies for sustainable management of sandy Sahelian soils. FAO repository. Regional office for Asia and the pacific, 2007.
(10.) Tabo R, Bationo A, Diallo MK, Hassane O and S Koala Fertilizer micro dosing for the prosperity of small-scale farmers in the Sahel. Final Report, ICRISAT, Niamey, 2005.
(11.) Fatondji D, Martius C, Bielders CL, Vlek PLG, Bationo A and B Gerard Effect of planting technique and amendment type on pearl millet yield, nutrient uptake, and water use on degraded land in Niger. Nutr Cycl Agroecosyst. 2007; (76): 203-217.
(12.) Wildemeersch J, Timmerman E, Mazijn B, Sabiou M, Ibro G, Garba M and W Cornelis Assessing the constraints to adopt water and soil conservation techniques in Tillaberi, Niger. Land Degrada &. Development. 2015; (26): 491-501.
(13.) Ndjeunga J and MSC Bantilan Uptake of improved technologies in the semi-arid tropics of West Africa: Why is agricultural transformation lagging behind? E-Journal of Agricultural and Development Economics. 2005; 2 (1): 85-102.
(14.) Schlecht E, Buerkert A, Tielkes E and A Bationo A critical analysis of challenges and opportunities for soil fertility restoration in Sudan-Sahel, West Africa. Nutr Cycl Agroecosyst. 2006; 76 (2-3): 109-136.
(15.) Aura S Determinants of the Adoption of integrated soil fertility management-technologies in Mbale division Kenya. African Journal of Food, Agriculture, Nutrition and Development. 2016; 16 (1): 10697-10710.
(16.) De Rouw A Improving yield and reducing risks in pearl millet farming in the African Sahel. Agricultural systems. 2004; (81): 73-93.
(17.) Abdoulaye T and JH Sanders Stages and determinants of fertilizer use in semiarid African agriculture: the Niger experience. Agricultural Economics. 2005; (32):167-179.
(18.) Kelly V Farmer's demand for fertilizer in Sub-Saharan Africa. Department of Agricultural economics, Michigan State University, East Lansing, MI. 2005; (48): 824-1039.
(19.) Bationo A and A Buerkert Soil organic carbon management for sustainable land use in Sudano-Sahelian West Africa. Nutr. Cycl. Agroecosyst. 2001; (61): 131-142.
(20.) Bayu W, Rethman NFG and PS Hammes The role of animal manure in sustainable soil fertility management in Sub-Saharan Africa. J Sustain Agric. 2004; 25 (2): 113-135.
(21.) Ouedraogo E Soil quality improvement for crop production in semi- arid West Africa. PhD Thesis, Department of Environmental Sciences, Erosion and Soil and Water Conservation Group, Wageningen University, Wageningen, the Netherlands, 2004.
(22.) Schlecht E and A Buerkert Organic inputs and farmers' management strategies in millet fields of western Niger. Geoderma. 2004; (121): 271-289.
(23.) Shepherd KD and MJ Soule Soil fertility management in West Kenya: dynamic simulation of productivity, profitability and sustainability at different resource endowment levels. Agricultural Ecosystem and Environment. 1998; (71): 131-145.
(24.) Masvaya EN, Nyamangara J, Nyaswasha RW, Zingore S, Delve RJ and KE Giller Effect of farmer resource endowment and management strategies on spatial variability of soil fertility in contrasting agro ecological zones in Zimbabwe. In: Bationo A, Waswa BS, Okeyo JM, Maina F and Kihara JM (Eds) Innovations as key to green revolution in Africa. 2011; (2): 1221-1229.
(25.) Mugwe J, Mugendi D, Mucheru-Muna M, Merckx R, Chianu J and B Vanlauwe Determinants of the decision to adopt integrated soil fertility management practices by smallholder farmers in the central highlands of Kenya. Expl. Agric. 2009; (45): 61-75.
(26.) Abdou A, Koala S and A Bationo Long-term soil fertility trials in Niger, West Africa. In: Bationo A, Waswa B, Kihara J, Adolwa I, Vanlauwe B, Koala S, editors. Lessons learned from long-term soil fertility management experiments in Africa. Springer Netherlands, 2011; 1-31.
(27.) International Union of Soil Sciences Working Group World Reference Base for Soil Resources. International soil classification system for naming soils and creating legends for soil maps. FAO, World Soil Resources Reports No. 106, Rome, Italy, 2014.
(28.) Soil Survey Staff Keys to Soil Taxonomy, 12th edition. Washington (DC): USDA-Natural Resources Conservation Service, 2014.
(29.) Food and Agricultural Organization of United Nations. FAO. Production yearbook, No. 39, Rome, Italy, 1985.
(30.) Cecchi G, Wint W, Shaw A, Marletta A, Mattioli R and T Robinson Geographic distribution and environmental characterization of livestock production systems in Eastern Africa. Agriculture, Ecosystem and Environment. 2010; (135): 98-110.
(31.) Kassie M, Jaleta M, Shiferaw B and F Mmbando Plot and household-level determinants of sustainable agricultural practices in rural Tanzania. Environment for Development, Discussion Paper Series, January 2012.
(32.) Institut National de la Statistique du Niger - INS La population du Niger, Ministere de l'economie et de finance, Niamey, Niger, 2012.
(33.) Salifu A, Lee Funk R, Keefe M and S Kolavalli Farmer Based organizations in Ghana. International Food Policy Research Institute Working Paper. 2012; (31): 1-16.
(34.) Kebeney SJ, Msanya BM, Semoka JMR, Ngetich WK and AK Kipkoech Socio-economic factors and soil fertility- management practices affecting sorghum production in Western Kenya: A case study of Busia County. American Journal of Experimental Agriculture. 2015; 5 (1): 1-11.
(35.) Martey E, Wiredu AL, Etwire PM, Fosu M, Buah SSJ, Bidzakin J, Ahiabor BDK and F Kusi Fertilizer adoption and use intensity among smallholder farmers in Northern Ghana: a case study of the AGRA Soil Health Project. Sustainable Agriculture Research. 2014; 3 (1): 24-36.
(36.) Adolwa IS, Schwarze S, Waswa B and A Buerkert Understanding system innovation adoption: a comparative analysis of integrated soil fertility management uptake in Tamale (Ghana) and Kakamega (Kenya). Renewable Agric. Food Syst. 2017. https://doi.org/10.1017/S1742170517000485 . (Published online 2nd October, 2017).
(37.) Duflo E, Michael K and R Jonathan Nudging farmers to use chemical fertilizer: Theory and experimental evidence from Kenya. American Economic Review. 2011; 101 (6): 2350-90.
(38.) Rhissa Z Revue du secteur de l'elevage au Niger. Rapport provisoire (FAO/OMS) 2010, 115p.
(39.) INS. Institut National de la Statistique Republique du Niger. Ministere des Finances- Indice Harmonise des Prix a la Consommation (IHPC) Niamey--Mars 2014.
Garba M (1*), Bakang J-E A (2), Sabiou M (1) and V Logan (3)
(*) Corresponding author email: firstname.lastname@example.org
(1)Institut National de la Recherche Agronomique du Niger (INRAN), B.P. 429 Niamey, Niger
(2) Department of Agric. Econs, Agribusiness & Extension, Kwame Nkrumah University of Science and Technology (KNUST), Kumasi, Ghana
(3) Department of Crop and Soil Science, Kwame Nkrumah University of Science and Technology (KNUST), Kumasi, Ghana
Table 1: Descriptive information of participant and non-participant respondents of the demonstration Statistics Characteristics Participant Non- participant Units s s Number of respondents 17 84 Number House hold size (persons 13.65 8.98 Mean Gender Male 100 98.02 Percentage Female 0 1.98 Percentage Educational Level No formal education 29.4 42.9 Percentage Primary education 5.9 4.8 Percentage Secondary education 5.9 2.4 Percentage Koranic education 52.9 39.3 Percentage Adult literate 5.9 6.0 Percentage Affiliation to Farmer - Based Organization Members 68.8 54.8 Percentage Non-members 31.3 45.2 Percentage Assets TLU 0.83 1.2 Mean Cart 0.88 1.52 Mean Radio 0.82 0.64 Mean TV 0.00 0.18 Mean Bicycle 0.18 0.19 Mean Motorcycle 0.00 0.02 Mean Land Area 6.32 6.43 Ha Wealth Total Estimated Household Wealth in Fcfa 725676.4 764391.4 Mean Farm income in Fcfa < 100 000 29.4 16.7 Percent 100 001 - 300 000 41.2 58.3 Percent 300 001 - 500 000 17.6 14.3 Percent > 500 000 11.8 9.5 Percent Table 2: Descriptive information on soil fertility management practices among demonstration participant and non-participant respondents Statistics Participants Non-participants Units Mineral fertilizer Use mineral 100 (yes) 70 (yes) Percentage fertilizer Organic fertilizer Use corralling 12 (yes) 18 (yes) Percentage Use straw mulch 65 (yes) 46 (yes) Percentage Method of cultivation Use hoe 31 (yes) 76 (yes) Percentage Use hoe and animal 69 (yes) 24 (yes) Percentage plough Table 3: Logistic regression, socioeconomic characteristics of farmers correlate soil fertility-management practices Independent Apply Purchase variables chemical chemical Fertilizer 1.22 (0.94) (a) fertilizer Village status 1.01 (0.93) Education level 0.04 (0.17) -0.02 (0.18) Participation to project 19.13 (8592) -6.53 (**)(1.67) Membership to FBO 2.26 (**) (1.03) 1.83 (1.09) Area 0.04 (0.14) -0.12 (0.09) Family size 0.05 (0.15) 0.02 (0.13) Family labour -0.26 (0.26) -0.13 (0.24) Hired labour 0.41 (0.98) 1.47 (1.05) TLU 0.10 (0.28) 0.40 (0.35) Cart 1.50 (**) (0.72) 1.67 (**)(0.76) Radio -0.51 (0.81) -0.98 (0.88) TV -0.15 (0.75) -1.00 (0.86) Bicycle 0.61 (1.08) 3.39 (**)(1.51) Motorcycle 0.13 (1.18) 2.77 (*) (1.49) Resource endowment -0.53 (0.98) -1.81 (*) (1.04) Average farm income 2.40 (*) (1.34) 2.00 (*) (1.18) Constant -1.50 (1.11) -1.03 (1.05) Likelihood ratio (LR) tests 69.65 (***) 63.34 (***) Nagelkerke [R.sup.2] 0.58 0.69 Cox & Snell [R.sup.2] 0.39 0.51 Dependent variables Independent Apply straw Use hoe variables mulch cultivation Village status -0.47 (0.78) -6.23 (**)(1.96) Education level 0.34 (*) (0.18) -0.24 (0.31) Participation to project -0.33 (0.99) 0.32 (1.48) Membership to FBO 2.51 (***)(0.96) -1.05 (1.25) Area 0.11 (0.09) -0.08 (0.07) Family size 0.23 (*) (0.12) -0.47 (**)(0.18) Family labour -0.46 (0.30) -0.18 (0.50) Hired labour 0.78 (0.75) -3.91 (**) (1.69) TLU 0.11 (0.22) 0.48 (*) (0.29) Cart 0.63 (0.81) -3.38 (**) (1.57) Radio 1.34 (0.84) -0.08 (1.65) TV -0.85 (1.15) 1.41 (2.07) Bicycle 1.78 (*) (0.91) -2.12 (1.66) Motorcycle -1.55 (1.00) 3.49 (*) (1.97) Resource endowment -2.38 (**)(1.13) -4.48 (**) (1.85) Average farm income 2.97 (**) (1.18) -0.58 (1.56) Constant -5.35 (**)(1.51) 17.30 (***)(5.22) Likelihood ratio (LR) tests 68.84 (***) 33.82 (***) Nagelkerke [R.sup.2] 0.66 0.84 Cox & Snell [R.sup.2] 0.49 0.59 Apply special Independent work variables Village status -2.98 (**)(0.94) Education level 0.31 (0.19) Participation to project -1.41 (1.08) Membership to FBO 3.24 (***)(1.18) Area 0.23 (**) (0.11) Family size 0.02 (0.10) Family labour 0.11 (0.31) Hired labour -0.15 (0.86) TLU 0.05 (0.15) Cart 0.40 (0.83) Radio 0.19 (0.90) TV -1.84 (1.33) Bicycle -0.07 (1.01) Motorcycle -0.82 (1.05) Resource endowment -0.07 (0.99) Average farm income 2.48 (**) (1.10) Constant -4.41 (**)(1.46) Likelihood ratio (LR) tests 66.60 (***) Nagelkerke [R.sup.2] 0.57 Cox & Snell [R.sup.2] 0.40 (a) Values in parentheses represent [+ or-] standard error; (*) P<0.10; (**) P<0.05; (***) P<0.01 (b) TLU is Tropical Livestock Unit, where one TLU is equivalent to 250 kg of biomass. The conversion factors used were as follows: 0.7 for cattle, 0.5 for donkey, 0.10 for sheep and goat, and 0.01 for chicken
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|Author:||Garba, M.; Bakang, J.-E.A.; Sabiou, M.; Logan, V.|
|Publication:||African Journal of Food, Agriculture, Nutrition and Development|
|Date:||Feb 1, 2020|
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