Abstract
This review paper focuses on the current state of poultry waste generation, composition, and management techniques in commercial poultry farms and trading in Bangladesh, to reduce pollution and generate economic benefits from poultry waste. It also underlines the negative impact of poultry waste disposal on the environment. In Bangladesh, collection of poultry waste into bags and, subsequently, direct use as fertilizer in agricultural fields and aquaculture is common, while alternative disposal methods such as composting and biogas generation are now attracting commercial poultry producers. Direct use of poultry manure results in poor air and soil quality, environmental deterioration, detrimental effects on global health, climate change due to high levels of atmospheric ammonia, and the creation of significant amounts of greenhouse gases. Lack of knowledge and investment, as well as high demand for free land for composting, are important obstacles. Future research on precise waste characterization, improved understanding of poultry waste management, and increased efforts on developed waste disposal for a safe environment are therefore recommended. So, poultry waste, which is currently a burden for the environment, could be turned into a useful agricultural resource, which would be useful for the poultry industry.
Keywords: Poultry waste, waste generation and utilization in Bangladesh, environmental impact, modern technology, waste mitigation
Introduction
Poultry is an important subsector of the livestock industry and the fastest-growing agricultural enterprise in Bangladesh. It contributes significantly to the economy of Bangladesh by providing employment opportunities in rural and semiurban areas, as well as accessible protein sources for the growing population [1]. Poultry production has grown from 91 million in 1,990 to 365.85 million in the fiscal year of 2020–2021, owing to the huge demand for poultry meat and eggs [2,3].
Bangladesh has a long history of poultry production in traditional backyard farming. Initially, poor rural women and unemployed youngsters were involved in commercial poultry rearing on a modest scale. It also included semiurban and urban poultry raisers who contributed to meeting the growing demand for eggs and meat. Since 1990, the commercial poultry sector has grown at a steady pace of 15%–20% per year, with a slight slowdown after 2007 due to the avian influenza outbreak by Hamid et al.[4], contributing about 1% of the country’s gross domestic product (GDP) [1]. However, the overall investment in the poultry business in 2019 was around 3.7 billion Bangladeshi taka or 42 million USD (Larive International B.V. and Light Castle Partners Ltd., 2020), and commercial poultry production was carried out on around 150,000 farms [1].
Poultry production, on the other hand, is a complicated process that combines the economic, social, and environmental aspects of a given product within a socioeconomic context. Unfortunately, as poultry production has become more concentrated and operation sizes have expanded, major environmental challenges have arisen [5]. Despite their great socioeconomic benefits in terms of egg production, meat production, and employment generation, they also endanger human and animal lives by polluting water, land, and air[6–8].
The primary issue facing the poultry industry is the large-scale accumulation of wastes [9] from hatcheries and slaughterhouses (water and organic solid by-products) of live bird markets (LBM). Poor waste management can cause health and welfare problems in flocks, bad smells, fly breeding, and contamination of land and water [10,11].
As a result, poultry waste management is essential for environmental protection, human health and safety, and safe poultry production. Such a significant volume of waste may cause disposal and pollution difficulties unless environmentally and economically sustainable alternatives are discovered. Resolving these issues requires serious attention to managing poultry waste so that the environmental impacts of such a huge volume of waste are minimized.
Therefore, this review focuses on the current state of the commercial poultry waste management practices in Bangladesh, emphasizing their significance as well as proposing a successful guideline to manage the waste properly. Researchers or scientists will quickly understand what is happening, which will help improve waste management and a recycling system that will last.
Characterization and Quantification of Poultry Waste
Poultry wastes or manure consist of excreta, feathers, spilled feeds and water, dead birds, broken eggs, wastewater, litter or bedding materials (i.e., rice husk, sawdust, wood shavings, peanut hulls, straw, etc.), dead birds, and slaughterhouse and hatchery wastes. The primary components of poultry wastes are water and carbon; small amounts of nitrogen and phosphorous; and trace amounts of chlorine, calcium, magnesium, sodium, manganese, iron, copper, zinc, potassium, arsenic, cobalt, selenium, molybdenum, and boron [9,12,13].
According to previous research, offal (slaughterhouse waste) contains 5.3% of the total Kjeldahl nitrogen, 32% protein, 54% lipids, and 0.6%–0.9% methane (CH4) generation potential, whereas chicken feathers contain approximately 91% protein (mostly keratin), 1% lipids, and 8% water [8]. The detailed chemical composition of poultry and hatchery waste is shown in Table 1.
Table 1. Chemical composition of poultry and hatchery wastes.
Particulars | Poultry waste | Hatchery waste | Source |
---|---|---|---|
Dry matter % | N/A | 94.66–97.35 | [14–20] |
pH | 6 | N/A | |
Metabolizable energy (Kcal/kg) | N/A | 2,914 | |
Crude protein % | N/A | 22.80–44.58 | |
Crude fiber % | N/A | 0.58–8.06 | |
Ether extract % | N/A | 11.43–30.00 | |
Nitrogen-free extract % | N/A | 21.31–23.98 | |
Ash % | N/A | 14.00–40.00 | |
Organic carbon% | 35.4 | N/A | |
Nitrogen % | 3.52 | N/A | |
Phosphorus % | 0.86 | 0.39–0.84 | |
Potassium % | 1.83 | N/A | |
Calcium % | 0.45–2.05 | 7.26–22.60 | |
Magnesium % | 0.215–0.51 | N/A | |
Iron (ppm) | 950–1050 | N/A | |
Manganese (ppm) | 80–240 | N/A | |
Zinc (ppm) | 70–230 | N/A | |
Copper (ppm) | 12–60.4 | N/A |
Note: N/A, Information not available
According to the Agricultural Census 2008, there was about 137.23 million poultry in Bangladesh. The total annual fresh poultry litter production was 4.52 million tons, of which 3.10 million tons were produced under commercial poultry farming [21]. A study argued that Bangladesh produces 1.56 million tons of poultry manure annually [22]. According to the International Finance Corporation, around 2,000 million chickens in Bangladesh produce about 2.2 million tons of manure annually [23]. Another recent study found that the country’s 312 million poultry produce 2.1 million tons of poultry waste (dry matter) yearly [24]. Specifically, a layer flock of 3,000 birds produces 300 kg of feces per day while consuming 500 kg of feed, resulting in 0.1 kg/bird/day waste generation. Another study that claimed a flock of 10,000 laying hens would produce one metric ton of waste daily supports the above findings [25,26]. On average, on a farm, commercial layer, broiler, or breeder poultry excretes 0.07–0.178 kg of feces per day. However, the feces production range indicates a lot of fluctuation due to differences in feed intake, water consumption, environment, bird age, composition, and feed form[17,19,27–29].
Usage of Poultry Waste in Bangladesh
Feathers, offal, and litter from poultry are valuable agricultural wastes because they contain nutrients and are a rich source of protein. They can be made into valuable products like feather meal, biodiesel, biodegradable plastic, fertilizer, or manure [13].
Application as fertilizer
Poultry litter is an excellent organic fertilizer for enhancing soil fertility, root system development, and plant vigor, as well as making the plant more resistant to diseases and pest infestations [30,31]. Direct application of poultry waste in crop fields, on the other hand, can cause soil, air, and water quality concerns that are yet to be investigated. Most of the poultry manure and litter are currently applied to agricultural land, making it the preferred and practical method in developing nations [32,33]. Surface and groundwater become polluted because of the potential pollutants in the manure and litter, and agricultural yields drop when there is a lot of manure and trace elements [13].
Composting
Composting, an anaerobic conversion process that turns organic compounds into a soil-friendly product in a controlled manner, is one of the most successful and widely used methods for dealing with poultry waste [13,34,35]. Composting has several advantages, including the slow release of nutrients, lower pathogen levels, less potential to degrade water quality, fewer weed seeds, improved soil fertility, reduced fly infestations, and foul odor [21,34,36]. Composting, on the other hand, necessitates land, financial investment, labor, and management and emits harmful CH4 gas as it decomposes [34,35,37]. However, vermicompost could be a better option that minimizes the environmental effect. Vermicompost is created by decomposing poultry waste and bedding materials by various worms, typically red wigglers, white worms, and other earthworms (https://www.adrabangladesh.org/). It is currently gaining popularity due to its superior quality for the soil, plants, and vegetable fields. Nowadays, private companies in Bangladesh are currently marketing vermicompost at a low cost to farmers (https://www.garden.com.bd/fertilizers/2-vermicompost-fertilizer.html).
Moreover, government and nongovernment organizations (NGOs), as well as research and extension institutes, such as Bangladesh Agricultural University and Bangladesh Agriculture Research Institute, are bridging farmers’ access to the most appropriate and cost-effective composting technologies [37]. Private organizations, such as Waste Concern, Annapurna Agro Service, Grameen Shakti, Rural Development Academy, Innovation Consulting Pvt. Ltd., Rash Agro Enterprise, and Acme Laboratories, have evolved to work toward the commercial availability of compost in superstores in Bangladesh and the promotion of composting [37]. These organizations assist rural farmers in preparing compost by regulatory guidelines. Although the support is minimal, the capacity of waste supply for these private enterprises is insufficient. Wood ash, tea leaves, table scraps, sawdust, leaves, fruit and vegetable scraps, garden weeds, eggshells, and chicken manure are all used in these businesses. So, in those businesses, only a small amount of chicken waste is used to make compost.
Biogas
Biogas is a gas mixture formed by the anaerobic digestion of various organic materials. It is largely composed of CH4, carbon dioxide (CO2), and a trace amount of hydrogen sulfide [38,39]. Poultry wastes, leftover feeds, and wastewater from the premises can all be utilized to form a slurry (biomass) that can be supplied into a biogas plant for anaerobic fermentation to produce biogas [40,41]. Biogas and bio-slurry replace the cost of fuel (cooking, power, or both) and fertilizer [29,42]. Moreover, biogas plants reduce carbon emissions [29]. Bangladesh has a significant potential for producing biogas from poultry wastes as it can build at least 4 million biogas plants, which could produce 105 billion cubic feet of biogas per year, equivalent to 1.5 million tons of kerosene or 3.08 million tons of coal, and could meet the cooking and lighting needs of approximately 20% of the country’s households [43,44]. Approximately 91,350 home and commercial so-called biogas plants that use cattle and poultry manure as raw materials are currently available [24] in the country. Still, the energy production level from those biogas plants is unknown. Individual family biogas plants are currently available in Bangladesh for small- and medium-scale poultry producers, while commercial biogas plants are not yet well structured. Although biogas generated in anaerobic systems is useful for household and agricultural use, bio-slurry is bad for farmers and the environment [44]. Limestone is an essential ingredient of layer feeds, part of which usually passes through the feces and accumulates in slurry. The biogas plant’s digester gradually fills up with slurry-borne limestone, which also clogs the plant’s slurry drainage system, causing producers to stop operating. On the other hand, with regular use, the biogas plant becomes so dirty and smelly that it provokes complaints of odor from neighbors. These prevent Bangladesh from fully utilizing the advantages of its biogas plant (personal observation).
Biochar production
Using biochar, a solid formed from carbonized biomass, on land can enhance soil properties and lower greenhouse gas emissions brought on by biomass degradation [45]. In subtropical climates, poultry waste biochar can reduce nitrogen mineralization rates, resulting in higher nitrogen usage efficiency and crop yield [46,47]. It is made by pyrolyzing or gasifying biomass feedstock in an oxygen-depleted environment to create a stable, carbon-rich product resistant to soil deterioration. Poultry litter biochar is made from fresh poultry litter by pyrolyzing it for 10 min at 300°C in a muffle furnace with low oxygen. It can also be produced on a large scale using a simple biochar plant [48]. It contains higher nutrients than fresh poultry litter and hence is used on agricultural land as a long-term production management technique [45,47]. However, in Bangladesh, so far, the method is not being used to dispose of poultry waste. Also, the process is sensitive to changes in temperature, gas levels, pH, ash concentration, and tar content. This makes it hard to use biochar waste treatment methods.
Livestock feeds
Processed poultry litter is used in diets for poultry, swine, lambs, ewes, lactating cows, wintering cattle, and brood cows [49–51]. Feathers contain more than 90% protein and are a good source of hydrophobic amino acids like cysteine, arginine, and threonine; feathers are also processed into feather meal for animal feed, organic fertilizer, and feed supplements [8]. There is currently no feed company in Bangladesh that uses poultry litter as an ingredient in livestock feed.
Rendering (poultry meat and by-product processing)
Rendering is a process of both physical and chemical transformation that involves the use of a variety of equipment and processes, including the application of heat, de-moisturizing, and the separation of fat[52].Rendering transforms by-products of meat and poultry into marketable commodities such as edible and inedible fats and proteins for agricultural and industrial applications [53,54].It can produce meat-bone-meal, poultry by-product meal, and steam hydrolyzed feather meal for fish or livestock feed or used as fertilizer by further processing via anaerobic digestion or composting [55]. The materials used in the rendering process included viscera, meat scraps (including fat, bone, and blood), feathers, hatchery by-products (infertile eggs and dead embryos), and dead animals [53]. The rendering process is also not yet commercialized in Bangladesh.
In addition, there are many other uses of poultry waste, like preparation of biodiesel, reuse of litter, and mass burning or direct combustion. Feather meal is boiled in water at 70°C to remove the fat, which is then trans-esterified to produce biodiesel [8]. Reusing litter materials for broiler rearing is a popular idea in Bangladesh due to the cost-saving advantages of not completely replacing the leftover litter with a fresh bedding material for each batch [8]. Direct burning and incineration are well-known ways of generating renewable energy and ash from waste, and they have the potential to close the nutrient loop in the poultry industry [56]. None of these uses are being practiced in Bangladesh.
Present Scenario of Waste Management in Bangladesh
There are approximately 8 grandparent stocks, 100 breeder farms and hatcheries, and over 70,000 commercial layer and broiler farms in Bangladesh [57], producing 2.1 million tons of stinky manure each year [24], which provokes complaints of odor and flies from neighborhoods. The demand for manure in the country is seasonal and most of it is piled up for the rest of the year.
Farm waste
Generally, the large poultry breeder companies, such as Aftab Bahumukhi Farms Ltd., Nourish Poultry and Hatchery Ltd., Kazi Farms Group, Nahar Agro Ltd., Provita, Paragon Group, and others, have strong relationships with local brokers who collect spent litter and sell it to crop and fish farmers. These companies manage their poultry in contact housing, either in floor or slat cum floor systems, or in cage systems, with birds kept for 64–66 weeks (broiler breeders), 72–80 weeks (layer breeders), and approximately 90 weeks (layers). They usually practice proper poultry waste management, primarily through composting (Fig. 1). The litter and/or manure remain in the shed until the birds are culled. In a cage system, farmers routinely scrub the litter and keep it in a compost pit (Fig. 2), while some farmers store it in an open field. Small-scale commercial layer and broiler farms have haphazard poultry waste management, with the waste being utilized as fertilizer on neighboring agricultural land, piled at the roadside or near the shed, sold to the buyer, used as fish feed, or dumped in open areas (Fig. 3) without any treatment [3,27,58–60]. Due to economic effectiveness, farmers in the broiler production system frequently reuse their litter materials (rice husk) for two or more flocks, which result in poor quality poultry manure if not adequately dried, increasing the risk of disease outbreaks in that flock. In addition, litter from rural poultry farms is commonly deposited in nearby low-lying areas, resulting in greenhouse gas emissions as well as pollution of the water and air [25]. The majority of Bangladeshi poultry farms use litter as compost (52.78%), while others use it for fish feed (30.55%) and other purposes (8.33%). About 47.20% of the farms dispose of litter in pits, while 44.44% in open places, 5.56% on the roadside, and the rest 2.78% in other places, as reported previously [61]. Furthermore, poultry waste is disposed of in agricultural fields, open disposal pits, or open drains, and poultry carcasses are routinely disposed of or thrown near poultry sheds, where dogs and foxes scavenge for food [44,59].
Figure 1. Poultry litter management in a slat cum floor system of a breeder farm in Bangladesh. A) Poultry excreta under the slat area for a period of 66 weeks. B) Collected excreta from the shed for sale.
Figure 2. Poultry litter management in case of breeder or commercial layer farms in Bangladesh. A) and B) Litter for scrubbing out from the shed. C) Compost chamber. D) Anaerobic condition for preparing compost.
Figure 3. Traditional waste management practices in commercial layer and broiler farms in Bangladesh. A) Waste passing directly to the open pit. B) Before being sold, the litter is collected and stored beside the shed. C) Integrated layer and fish farm where the litter directly goes to the pond. D) Litter used in a nearby agricultural land.
In most cases, large commercial companies have their own disposal pit (Fig. 4) to dispose of dead and culled birds. Some poultry companies convert manure into organic fertilizer as it is becoming popular among vegetable producers. However, biogas plants are not yet established at most private companies because these plants require a lot of land and a huge investment to build. Kazi Farms Group (one of Bangladesh’s largest corporations) had previously established biogas units. Still, they were compelled to shut down the plants due to a lack of space on their own property for the large amounts of produced slurry. The stored slurry wastes rather flooded across the public’s land during the rainy season, resulting in a slew of compensation claims, prompting the company to shut down the biogas plant and compost organic fertilizer [26]. However, those companies may retreat slurries by vermicomposting, and they can be transformed into organic fertilizer, which has a high commercial value. Now, vermicompost from the slurry is sold at 10 USD/bag (100 kg).
Figure 4. Disposal pit for dead and culled birds of a breeder farm in Bangladesh. A) Top view. B) Side view.
Hatchery waste
The common hatchery wastes (Fig. 5) produced by the poultry hatchery are eggshells, broken eggs, infertile eggs, culled chicks, etc. Hatchery waste may be referred to as miscellaneous waste too. The traditional method of landfilling is widely used to dispose of hatchery waste throughout the country, while some companies donate embryos and culled chicks to catfish farming in ponds. Some hatcheries sell infertile eggs to bakeries for biscuits and cake preparation. Disposing of large-scale hatchery waste via landfilling is one of the key issues. As a result, the poultry sector is dealing with high land costs and a waste management problem. However, reducing hatchery waste for livestock feed production or other chemical companies (beauty soap, shampoo, conditioner, etc.) may contribute significantly to waste utilization without posing any environmental risks.
Figure 5. Hatchery wastes in Bangladesh. A) Candling of eggs in a hatchery that shows infertile eggs as clear eggs. B) Infertile egg fluid for dumping. C) Crushed eggshells after regular hatch out. D) Culled chicks immediately after hatch out.
Live bird market waste
During slaughtering and processing, retailers keep the offal and leftover chicken parts, except the feathers, and sell these as fish feed, chicken feces, feathers, and other solid chicken waste are disposed of in municipal waste disposal bins [59]. Poultry litter and leftover feed (kept at the retailer’s stall for rearing chickens before being sold) are frequently swept up, and part of these wastes adhere daily layer by layer on the surface of the floor; however, neither the market authority nor the shopkeeper care for them [59]. Other fowl parts, such as the liver, skin, and feet, are frequently sold directly to low-income community members for consumption. Because there is usually no authority to control the cleaning and disinfection method of the LBM, they are not cleaned and sanitized at the end of the day. This makes LBM the most likely place for pathogens to enter the environment and act as a hub for the spread of zoonotic avian pathogens in the community [58].
Overall, waste management practices by small- and medium-scale commercial farms are minimal, whereas large-scale producers try to maintain the scientific method. However, a lack of capital and insufficient land often impede the process. So, waste use in all types of poultry production in Bangladesh (breeder or commercial farms, hatchery, LBM) depends greatly on capital, technical knowledge, awareness, and available facilities (Fig. 6).
Figure 6. Graph illustrating the generation of poultry waste from various sources, as well as its management and utilization in Bangladesh. Black lines indicate production source; red lines indicate waste generation and management; and blue lines indicate utilization of poultry waste.
Impacts on the Environment and Health
Despite the huge benefits of poultry waste, now it is becoming an undisputable concern around the world. The constant production of poultry waste causes environmental annoyances that are hazardous to animal and human health [56,62–66]. Poultry farms have been linked to poor air quality and environmental degradation due to high atmospheric ammonia emitted from poultry litter [9,67–69]. Poultry waste is contributing to global climate change by emitting greenhouse gases, such as nitrous oxide, CO2, and CH4, through microbial activity and changes in temperature, pH, moisture, and oxygen concentrations [9,70–75]. Reportedly, these air pollutants could have a significant negative impact on both human and animal health, with a variety of illnesses like nose discomfort, breathing issues, and coughing [76–78]. Long-term exposure to sustained air pollution leads to allergic reactions and effects on life span [79,80]. However, the exact number of pollutants produced from poultry waste in Bangladesh remains unknown. Many countries have found that uncontrolled disposal of poultry manure in areas where chickens are raised is a major cause of environmental damage and contamination of the air, soil, and water [56].
Poultry litter may include human and animal infections, such as zoonotic avian influenza. Therefore, appropriate hygiene must be used when handling poultry manure [80,81]. Moreover, contaminated food or water by poultry waste may contain different pathogens and water pollutants [82,83] that cause gastrointestinal diseases like typhoid fever, cholera, and hepatitis E infections [84]. Different vectors, including mosquitoes, birds, insects, and rodents, spread various diseases through waste [85,86]. Poultry waste is typically discharged through a single channel waterline that connects to ponds and rivers, causing heavy metal pollution, antibiotic residues, and microbial contamination of surface and drinking water [87–91]. Furthermore, these lead to oxygen deprivation, which could speed up the rate of toxin compound accumulation, leading to water-borne and respiratory diseases [92]. In Bangladesh, the scenario is essentially comparable, and the improper disposal of untreated poultry waste outlined above will provide an overview of the environmental impacts connected with farm operations, hatcheries, and LBM, whether directly or indirectly. Poultry farms create smells that harm the lives of individuals who live nearby. In addition, poor litter management pollutes soil and water, acts as a solid medium for pathogenic bacteria to flourish, and releases harmful compounds that result in heavy metal contamination [60,71,93,94]. It has also been demonstrated that long-term use of poultry waste on soil causes an accumulation of microelements, potentially increasing the bioavailability and toxicity of metals in the environment [87–90]. So, proper disposal, management and use are needed to reduce risks to the environment and the health of poultry.
Conclusion and Recommendations
Scientific and safe methods of utilizing poultry waste and by-products have the potential to increase farmer revenue. In areas where intensive poultry production is practiced, and population density is high, improper poultry waste storage and disposal pose a risk of air and water pollution, as well as health hazards. Manure collection, treatment, storage, and effective utilization of poultry waste benefit the industry, the environment, and the country. The rendering process is commonly used to convert by-products into marketable products for agricultural and industrial uses [53]. The proper processing and treatment of waste material not only allows for the creation of useful and valuable by-products but also helps to save the environment. Therefore, policymakers need to consider the poultry production process and waste management in the country. For example, poultry farmers must have good facilities to dispose of their farm waste. The authority may encourage private sectors and NGOs to invest in and render the composting and biogas production processes for poultry waste or litter, LBM, and hatchery waste to render, recycle, or incinerate. The knowledge and skills of farmers can be increased through training and practice by extending services on proper poultry waste management. However, modern waste recycling, biogas plants, or composting methods require further research and implementation of the technologies at the farmer level. Government extension personnel should provide information on manure management, and successful intervention should occur through field trips, farm visits, or farmer meetings. They are highly recommended.
Perfectly managed poultry waste could be a valuable source of income and contribute to the country’s GDP, and will contribute to the United Nations Sustainable Development Goal. This is a very important problem that needs to be fixed because it is hurting the natural biological system. It should be brought to the attention of all poultry business owners and other important people.
Acknowledgments
The authors are thankful to the authority of Nourish Poultry and Hatchery Limited, Bangladesh. They declare that no funds, grants, or other support were received during the preparation of this manuscript.
List of Abbreviations
GDP, Gross domestic product; LBM, Live bird market; NGO, Nongovernment organization.
Conflict of interest
The authors have no relevant financial or nonfinancial interests to disclose.
Authors’ contributions
MMR wrote the first draft of the manuscript. MMR, AH, and IH searched the literature, collected the data, and simulated the information. MMR, AH, IH, MMRJ, EHC, and RP edited and critically reviewed the manuscript. RP planned, designed, and supervised the work. All authors have read and agreed to the published version of the manuscript.
References
- [1].Rahman M, Chowdhury E, Parvin R. Small-scale poultry production in Bangladesh: challenges and impact of COVID-19 on sustainability. German J Vet Res. 2021;1(1):19–27. https://doi.org/10.51585/gjvr.2021.0004. [Google Scholar]
- [2].Livestock economy at a glance 2020–2021. [17 August 2021]. Available via http://dls.portal.gov.bd/sites/default/files/files/dls.portal.gov.bd/page/ee5f4621_fa3a_40ac_8bd9_898fb8ee4700/2021-08-12-06-04-17afc6fe8ba7a0c2a7943d5b04e648ec.pdf .
- [3].Jabbar MA, Rahman M, Talukder RK, Raha S. Alternative institutional arrangements for contract farming in poultry production in Bangladesh and their impacts on equity. Int Livest Res Inst (aka ILCA and ILRAD) Res Rep. 2007. [17 August 2021]. Available via https://ideas.repec.org/p/ags/ilrirr/99125.html .
- [4].Hamid M, Rahman M, Ahmed S, Hossain K. Status of poultry industry in Bangladesh and the role of private sector for its development. Asian J Poult Sci. 2017;11(1):1–13. https://doi.dx.org/10.3923/ajpsaj.2017.1.13. [Google Scholar]
- [5].Rodić V, Perić L, Đukić-Stojčić M, Vukelić N. The environmental impact of poultry production. Biotechnol Anim Husb. 2011;27(4):1673–9. https://doi.dx.org/10.2298/BAH1104673R. [Google Scholar]
- [6].Sakar S, Yetilmezsoy K, Kocak E. Anaerobic digestion technology in poultry and livestock waste treatment—a literature review. Waste Manag Res. 2009;27(1):3–18. doi: 10.1177/0734242X07079060. https://doi.dx.org/10.1177/0734242X07079060. [DOI] [PubMed] [Google Scholar]
- [7].Hu Y, Cheng H, Tao S. Environmental and human health challenges of industrial livestock and poultry farming in China and their mitigation. Environ Int. 2017;107:111–30. doi: 10.1016/j.envint.2017.07.003. https://doi.dx.org/10.1016/j.envint.2017.07.003. [DOI] [PubMed] [Google Scholar]
- [8].Muduli S, Champati A, Popalghat HK, Patel P, Sneha K. Poultry waste management: an approach for sustainable development. Int J Adv Sci Res. 2019;4:08–14. [Google Scholar]
- [9].Kelleher B, Leahy JJ, Henihan A, O’dwyer T, Sutton D, Leahy M. Advances in poultry litter disposal technology–a review. Bioresour Technol. 2002;83(1):27–36. doi: 10.1016/s0960-8524(01)00133-x. https://doi.dx.org/10.1016/S0960-8524(01)00133-X. [DOI] [PubMed] [Google Scholar]
- [10].Coufal CD. Texas A&M University; College Station, TX: 2005. Quantification of litter production and the fate of nitrogen in commercial broiler production systems. [Google Scholar]
- [11].Tabler T, Liang Y, Wells J, Moon J. Mississippi State University Extension Service; 2021. [17 August 2021]. Broiler litter production and nutrient content characteristics. Available via http://extension.msstate.edu/publications/broiler-litter-production-and-nutrient-content-characteristics . [Google Scholar]
- [12].Dróżdż D, Wystalska K, Malińska K, Grosser A, Grobelak A, Kacprzak M. Management of poultry manure in Poland–current state and future perspectives. J Environ Manag. 2020;264:110327. doi: 10.1016/j.jenvman.2020.110327. https://doi.dx.org/10.1016/j.jenvman.2020.110327. [DOI] [PubMed] [Google Scholar]
- [13].Thyagarajan D, Barathi M, Sakthivadivu R. Scope of poultry waste utilization. IOSR J Agric Vet Sci. 2013;6(5):29–35. https://doi.dx.org/10.9790/2380-0652935. [Google Scholar]
- [14].Zayed MS, Hassanein M, Esa NH, Abdallah M. Productivity of pepper crop (Capsicum annuumL.) as affected by organic fertilizer, soil solarization, and endomycorrhizae. Ann Agric Sci. 2013;58(2):131–7. https://doi.dx.org/10.1016/j.aoas.2013.07.011. [Google Scholar]
- [15].Swain BK, Naik PK, Singh NP. Unconventional feed resources for efficient poultry production. ICAR-ICAR Research Complex for Goa, Goa, India, 2014. Report No.: Technical Bulletin No 47. Available via chrome-extension://efaidnbmnnnibpcajpcglclefindmkaj/https://ccari.icar.gov.in/Technical%20Bulletin%20No.%2047.pdf.
- [16].Abiola S, Radebe N, vd Westhuizen C, Umesiobi D. Whole hatchery waste meal as alternative protein and calcium sources in broiler diets. Arch Zoot. 2012;61(234):229–34. https://doi.dx.org/10.4321/S0004-05922012000200007. [Google Scholar]
- [17].Amanullah MM, Sekar S, Muthukrishnan P. Prospects and potential of poultry manure. Asian J Plant Sci. 2010;9(4):172–82. https://doi.dx.org/10.3923/ajps.2010.172.182. [Google Scholar]
- [18].Rahman M, Akter M, Howlider M. Replacement of fish meal by hatchery wastes in broilers diets. Bangladesh Vet. 2003;20(1):29–35. [Google Scholar]
- [19].Wiliams C, Barker J, Sims J. Management and utilization of poultry wastes. Rev Environ Contam Toxicol. 1999. pp. 105–57. https://doi.dx.org/10.1007/978-1-4612-1528-8_3. [DOI] [PubMed]
- [20].Dhaliwal A, Shingari B, Sapra K. Chemical composition of hatchery waste. Pak Vet J. 1997;17:168–70. [Google Scholar]
- [21].MFL. Government of the people’s republic of Bangladesh Ministry of Fisheries and Livestock: Ministry of Fisheries and Livestock. Ministry of Fisheries and Livestock; Bangladesh: 2015. Draft national integrated livestock manure management (ILMM) policy, 2015. [Google Scholar]
- [22].Miah MR, Rahman AKML, Akanda MR, Pulak A, Rouf MA. Production of biogas from poultry litter mixed with the co-substrate cow dung. J Taibah Univ Sci. 2016;10(4):497–504. https://doi.dx.org/10.1016/j.jtusci.2015.07.007. [Google Scholar]
- [23].Rahman S. The Daily Star; Bangladesh: 2012. [17 August 2021]. Poultry litter can ease energy crisis. Available via https://www.thedailystar.net/news-detail-219726 . [Google Scholar]
- [24].Sabbir AYB, Saha CK, Nandi R, Zaman MFU, Alam MM, Sarker S. Effects of seasonal temperature variation on slurry temperature and biogas composition of a commercial fixed-dome anaerobic digester used in Bangladesh. Sustainability. 2021;13(19):11096. https://doi.dx.org/10.3390/su131911096. [Google Scholar]
- [25].Mainali B, Emran SB, Silveira S. Greenhouse gas mitigation using poultry litter management techniques in Bangladesh. Energy. 2017;127:155–66. https://doi.dx.org/10.1016/j.energy.2017.03.103. [Google Scholar]
- [26].Ovi I, Amin M. Turning chicken manure into organic fertilizer. 2019. [17 August 2021]. Available via https://archive.dhakatribune.com/business/2019/01/17/turning-chicken-manure-into-organic-fertilizer .
- [27].Abdullah-Al-Amin M, Rahman M, Howlider M, Ahmed M. Disposal of layer droppings reared in case and impact on environmental pollution. J Bangl Agric Univ. 2009;7(452–2016–35804) https://doi.dx.org/10.3329/jbau.v7i2.4735. [Google Scholar]
- [28].Sun C, Wu H. Assessment of pollution from livestock and poultry breeding in China. Int J Environ Stud. 2013;70(2):232–40. https://doi.dx.org/10.1080/00207233.2013.773716. [Google Scholar]
- [29].Hossain MR. Can small-scale biogas projects mitigate the energy crisis of rural Bangladesh? A study with economic analysis. Int J Sustain Energy. 2020;39(8):744–60. https://doi.dx.org/10.1080/14786451.2020.1749056. [Google Scholar]
- [30].Shaji H, Chandran V, Mathew L. Book. Controlled release fertilizers for sustainable agriculture. Elsevier; Amsterdam, The Netherlands: 2021. Organic fertilizers as a route to controlled release of nutrients; pp. 231–45. https://doi.dx.org/10.1016/B978-0-12-819555-0.00013-3. [Google Scholar]
- [31].Ogbuewu I, Odoemenam V, Omede A, Durunna C, Emenalom O, Uchegbu M, et al. Livestock waste and its impact on the environment. [17 August 2021];Sci J Rev. 2012 1(2):17–32. Available via https://www.academia.edu/2712511/Livestock_waste_and_its_impact_on_the_environment . [Google Scholar]
- [32].Bolan NS, Szogi A, Chuasavathi T, Seshadri B, Rothrock M, Panneerselvam P. Uses and management of poultry litter. World’s Poult Sci J. 2010;66(4):673–98. https://doi.dx.org/10.1017/S0043933910000656. [Google Scholar]
- [33].Williams CM. Poultry waste management in developing countries: the role of poultry in human nutrition. FAO. 2013:46. [Google Scholar]
- [34].Said M. IOP conference series: earth and environmental science. 1. Vol. 492. IOP Publishing; Bristol, UK: 2020. Livestock waste and its role in the composting process: a review; p. 012087. https://doi.dx.org/10.1088/1755-1315/492/1/012087. [Google Scholar]
- [35].Singh P, Mondal T, Sharma R, Mahalakshmi N, Gupta M. Poultry waste management. Int J Curr Microbiol Appl Sci. 2018;7(08):701–12. https://doi.dx.org/10.20546/ijcmas.2018.708.077. [Google Scholar]
- [36].Tiquia SM, Tam NF. Characterization and composting of poultry litter in forced-aeration piles. Process Biochem. 2002;37(8):869–80. https://doi.dx.org/10.1016/S0032-9592(01)00274-6. [Google Scholar]
- [37].Sultana MM, Kibria MG, Jahiruddin M, Abedin MA. Composting constraints and prospects in Bangladesh: a review. J Geosci Environ Protect. 2020;8(09):126. https://doi.dx.org/10.4236/gep.2020.89008. [Google Scholar]
- [38].Dobre P, Nicolae F, Matei F. Main factors affecting biogas production-an overview. Romanian Biotechnol Lett. 2014;19(3):9283–96. [Google Scholar]
- [39].Stern S, Krishnakumar B, Charati S, Amato W, Friedman A, Fuess D. Performance of a bench-scale membrane pilot plant for the upgrading of biogas in a wastewater treatment plant. J Membr Sci. 1998;151(1):63–74. https://doi.dx.org/10.1016/S0376-7388(98)00238-5. [Google Scholar]
- [40].Singh G, Shamsuddin M, Lim S. IOP conference series: materials science and engineering. IOP Publishing; Bristol, UK: 2018. Characterization of chicken manure from Manjung region; p. 012084. https://doi.dx.org/10.1088/1757-899X/458/1/012084. [Google Scholar]
- [41].Wankhade P, Talokar A, Gourkhede D, Sakhare D, Verma D. Utilization of livestock waste to enhance farmers’ wealth. Economics. 2020;72:84–6. [Google Scholar]
- [42].Arshad M, Bano I, Khan N, Shahzad MI, Younus M, Abbas M, et al. Electricity generation from biogas of poultry waste: an assessment of potential and feasibility in Pakistan. Renew Sust Energ. 2018;81:1241–6. https://doi.dx.org/10.1016/j.rser.2017.09.007. [Google Scholar]
- [43].Shariar KF, Al Bustam H. Waste to energy: a new dimension in generating electricity in Bangladesh. Int J Eng Technol. 2012;4(4):480. https://doi.dx.org/10.7763/IJET.2012.V4.415. [Google Scholar]
- [44].Khanam JS, Huque KS, Huda N, Bashar MK. Management approach of livestock manure in present farming system of Bangladesh. Asian J Med Biol Res. 2019;5(1):63–70. https://doi.dx.org/10.3329/ajmbr.v5i1.41047. [Google Scholar]
- [45].Draper K, Tomlinson T. Poultry litter biochar—a US perspective. International Biochar Initiative. 2012. [17 August 2021]. Available via https://www.biochar-international.org/wp-content/uploads/2018/04/Poultry_litter_final_2012.pdf .
- [46].Uddin S, Islam MR, Jahangir MMR, Rahman MM, Hassan S, Hassan MM, et al. Nitrogen release in soils amended with different organic and inorganic fertilizers under contrasting moisture regimes: a laboratory incubation study. Agronomy. 2021;11(11):2163. https://doi.dx.org/10.3390/agronomy11112163. [Google Scholar]
- [47].Sikder S, Joardar J. Biochar production from poultry litter as management approach and effects on plant growth. Int J Recycl Org Waste Agric. 2019;8(1):47–58. https://doi.dx.org/10.1007/s40093-018-0227-5. [Google Scholar]
- [48].Shamim M, Uddin N, Hossain SAAM, Ruhul A, Mete FZ, Hiemstra T. Production of biochar for soil application: a comparative study of three kiln models. Pedosphere. 2015;25(5):696–702. https://doi.dx.org/10.1016/S1002-0160(15)30050-3. [Google Scholar]
- [49].Hadjipanayiotou M, Labban LM, Kronfoleh A, Verhaeghe L, Naigm T, Al-Wadi M, et al. Studies on the use of dried poultry manure in ruminant diets in Syria. [17 August 2021];Livest Res Rural Dev. 1993 5(1):1–7. Available via http://www.lrrd.org/lrrd5/1/syria2.htm . [Google Scholar]
- [50].Mullenix K, Stanford K, Rankins D, Ruffin BG, Norwood J, Dyke V, et al. Feeding broiler litter to beef cattle. 2020. [17 August 2021]. Available via https://www.aces.edu/blog/topics/beef/feeding-broiler-litter-to-beef-cattle/
- [51].Komolafe A, Sonaiya E. Simple processing method for recycling poultry waste into animal feed ingredient. Int J Appl Agric Apic Res. 2014;10(1–2):21–32. [Google Scholar]
- [52].Meeker D, Hamilton C. An overview of the rendering industry. In: Meeker DL, editor. Essential rendering: all about the animal by-products industry. National Renderers Association; Alexandria, VA: 2006. pp. 1–16. https://doi.dx.org/10.1002/047167849X.bio073.pub2. [Google Scholar]
- [53].Jayathilakan K, Sultana K, Radhakrishna K, Bawa A. Utilization of byproducts and waste materials from meat, poultry and fish processing industries: a review. J Food Sci Technol. 2012;49(3):278–93. doi: 10.1007/s13197-011-0290-7. https://doi.dx.org/10.1007/s13197-011-0290-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [54].Bisplinghoff FD. A history of North American rendering. Essent Rendering. 2006:17. [Google Scholar]
- [55].Campos I, Valente LMP, Matos E, Marques P, Freire F. Life-cycle assessment of animal feed ingredients: poultry fat, poultry by-product meal and hydrolyzed feather meal. J Clean Prod. 2020;252:119845. https://doi.dx.org/10.1016/j.jclepro.2019.119845. [Google Scholar]
- [56].Gbotosho O, Burt PJ. Environmental and health impacts of poultry manure disposal methods: a case study of Lagelu and Egbeda local government areas in Oyo State, Nigeria. Int J Agric Sustain. 2013;11(1):38–51. https://doi.dx.org/10.1080/14735903.2012.700100. [Google Scholar]
- [57].Saleque MA, Ansarey F. Poultry industry: challenges and solutions. 2020. Available via https://www.daily-sun.com/printversion/details/502289/Poultry-Industry:-Challenges-and-Solutions .
- [58].Rimi N, Sultana R, Muhsina M, Uddin B, Haider N, Nahar N, et al. Biosecurity conditions in small commercial chicken farms, Bangladesh 2011–2012. EcoHealth. 2017;14(2):244–58. doi: 10.1007/s10393-017-1224-2. https://doi.dx.org/10.1007/s10393-017-1224-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [59].Alam MU, Rahman M, Islam MA, Asaduzzaman M, Sarker S, Rousham E, et al. Human exposure to antimicrobial resistance from poultry production: assessing hygiene and waste-disposal practices in Bangladesh. Int J Hyg Environ Health. 2019;222(8):1068–76. doi: 10.1016/j.ijheh.2019.07.007. https://doi.dx.org/10.1016/j.ijheh.2019.07.007. [DOI] [PubMed] [Google Scholar]
- [60].Modak M, Chowdhury EH, Rahman MS, Sattar MN. Waste management practices and profitability analysis of poultry farming in Mymensingh district: a socioeconomic study: poultry waste management, its impacts & BCA. J Bangl Agric Univ. 2019;17(1):50–7. https://doi.dx.org/10.3329/jbau.v17i1.40663 . [Google Scholar]
- [61].Hossain M, Ashrafuzzaman M, Iqbal M, Hossain M, Hoque M. A survey on poultry litter management system in different poultry farms of Bangladesh. Int J Biomass Resour. 2014;16(1):37–43. [Google Scholar]
- [62].Abioye A. Issues in agricultural and rural development proceedings of the training workshop on agricultural and rural development, Department of Agricultural Economics. Olabisi Onabanjo University; Ago-Iwoye, Nigeria: 1994. Livestock problems in Nigeria: problems and prospects; pp. 105–32. [Google Scholar]
- [63].Anon. Cornell Waste Management Institute; 2005. [17 August 2021]. Natural rendering: composting livestock mortality and butcher waste. Available via http://cwmi.css.cornell.edu/naturalrendering.htm . [Google Scholar]
- [64].Anosike V. Health implications of poultry waste utilization for urban agriculture: an ecohealth approach. Epidemiology. 2007;18(5):S53. https://doi.dx.org/10.1097/01.ede.0000276589.25195.73. [Google Scholar]
- [65].Akanni KA, Benson O. Poultry wastes management strategies and environmental implications on human health in Ogun state of Nigeria. Adv Econ Busin. 2014;2:164–71. https://doi.dx.org/10.13189/aeb.2014.020402. [Google Scholar]
- [66].Mozhiarasi V, Natarajan TS. Slaughterhouse and poultry wastes: management practices, feedstocks for renewable energy production, and recovery of value added products. Biomass Convers Biorefin. 2022. pp. 1–24. https://doi.dx.org/10.1007/s13399-022-02352-0. [DOI] [PMC free article] [PubMed]
- [67].Ritz C, Fairchild B, Lacy M. Implications of ammonia production and emissions from commercial poultry facilities: a review. J Appl Poult Res. 2004;13(4):684–92. https://doi.dx.org/10.1093/japr/13.4.684. [Google Scholar]
- [68].Oliveira MD, Sousa FC, Saraz JO, Calderano AA, Tinôco IFF, Carneiro APS. Ammonia emission in poultry facilities: a review for tropical climate areas. Atmosphere. 2021;12(9):1091. https://doi.dx.org/10.3390/atmos12091091. [Google Scholar]
- [69].Jose VM, Rosario MDI, Cristina LC. Phytotoxicity of uncomposted and composted poultry manure. Afr J Plant Sci. 2010;4(5):151–9. [Google Scholar]
- [70].Kulcu R, Ekinci K, Evrendilek F, Ertekin C. Long-term spatiotemporal patterns of CH4 and N2O emissions from livestock and poultry production in Turkey. Environ Monit Assess. 2010;167(1):545–58. doi: 10.1007/s10661-009-1071-x. https://doi.dx.org/10.1007/s10661-009-1071-x. [DOI] [PubMed] [Google Scholar]
- [71].Anderson K, Moore Jr PA, Martin J, Ashworth AJ. Evaluation of a novel poultry litter amendment on greenhouse gas emissions. Atmosphere. 2021;12(5):563. https://doi.dx.org/10.3390/atmos12050563. [Google Scholar]
- [72].Huque K, Khanam J, Amanullah S, Huda N, Bashar M, Vellinga T, et al. Study on existing livestock manure management practices in Bangladesh. Curr J Appl Sci Technol. 2017;22(2):1–9. https://doi.dx.org/10.9734/CJAST/2017/34675. [Google Scholar]
- [73].Loyon L. Overview of animal manure management for beef, pig, and poultry farms in France. Front Sustain Food Syst. 2018;2:36. https://doi.dx.org/10.3389/fsufs.2018.00036. [Google Scholar]
- [74].Kumar M, Prakash V. A review on solid waste: its impact on air and water quality. J Pollut Effect Control. 2020;8:252. [Google Scholar]
- [75].Zhang H. Animal manure can raise soil pH. Prod Technol. 1998;10:1–2. [Google Scholar]
- [76].Sankoh FP, Yan X, Tran Q. Environmental and health impact of solid waste disposal in developing cities: a case study of granville brook dumpsite, Freetown, Sierra Leone. J Environ Prot. 2013;4(7):665–70. https://doi.dx.org/10.4236/jep.2013.47076. [Google Scholar]
- [77].Donham KJ, Knapp L, Monson R, Gustafson K. Acute toxic exposure to gases from liquid manure. J Occupat Med. 1982;24(2):142–5. [PubMed] [Google Scholar]
- [78].Schiffman SS. Livestock odors: implications for human health and well-being. J Anim Sci. 1998;76(5):1343–55. doi: 10.2527/1998.7651343x. https://doi.dx.org/10.2527/1998.7651343x. [DOI] [PubMed] [Google Scholar]
- [79].Mayer D. The long-term impact of health on economic growth in Mexico, 1950–1995. J Intl Dev. 2001;13(1):123. https://doi.dx.org/10.1002/jid.764. [Google Scholar]
- [80].Chen Y, Ebenstein A, Greenstone M, Li H. Evidence on the impact of sustained exposure to air pollution on life expectancy from China’s Huai River policy. Proc Nat Acad Sci. 2013;110(32):12936–41. doi: 10.1073/pnas.1300018110. https://doi.dx.org/10.1073/pnas.1300018110. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [81].Hossen MS, Hoque Z, Nahar BS. Assessment of poultry waste management in Trishal upazila, Mymensingh. Res Agric Livest Fish. 2015;2(2):293–300. https://doi.dx.org/10.3329/ralf.v2i2.25013. [Google Scholar]
- [82].Gautam S, Bundela P, Pandey A, Awasthi M, Sarsaiya S. Diversity of cellulolytic microbes and the biodegradation of municipal solid waste by a potential strain. Int J Microbiol. 2012;2012:325907. doi: 10.1155/2012/325907. https://doi.dx.org/10.1155%2F2012%2F325907. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [83].Raman N, Narayanan DS. Impact of solid waste effect on ground water and soil quality nearer to Pallavaram solid waste landfill site in Chennai. Rasayan J Chem. 2008;1(4):828–36. [Google Scholar]
- [84].Cabral JP. Water microbiology. Bacterial pathogens and water. Int J Environ Res Public Health. 2010;7(10):3657–703. doi: 10.3390/ijerph7103657. https://doi.dx.org/10.3390/ijerph7103657. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [85].Brinkel J, Khan MH, Kraemer A. A systematic review of arsenic exposure and its social and mental health effects with special reference to Bangladesh. Int J Environ Res Public Health. 2009;6(5):1609–19. doi: 10.3390/ijerph6051609. https://doi.dx.org/10.3390/ijerph6051609. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [86].Ziraba AK, Haregu TN, Mberu B. A review and framework for understanding the potential impact of poor solid waste management on health in developing countries. Arch Public Health. 2016;74(1):1–11. doi: 10.1186/s13690-016-0166-4. https://doi.dx.org/10.1186/s13690-016-0166-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [87].Zhang J. The impact of water quality on health: evidence from the drinking water infrastructure program in rural China. J Health Econ. 2012;31(1):122–34. doi: 10.1016/j.jhealeco.2011.08.008. https://doi.dx.org/10.1016/j.jhealeco.2011.08.008. [DOI] [PubMed] [Google Scholar]
- [88].Vrzel J, Vuković-Gačić B, Kolarević S, Gačić Z, Kračun-Kolarević M, Kostić J, et al. Determination of the sources of nitrate and the microbiological sources of pollution in the Sava River Basin. Sci Total Environ. 2016;573:1460–71. doi: 10.1016/j.scitotenv.2016.07.213. https://doi.dx.org/10.1016/j.scitotenv.2016.07.213. [DOI] [PubMed] [Google Scholar]
- [89].Fan Y, Wang H, Deng L, Wang Y, Kang D, Li C, et al. Enhanced adsorption of Pb (II) by nitrogen and phosphorus co-doped biochar derived from Camellia oleiferashells. Environ Res. 2020;191:110030. doi: 10.1016/j.envres.2020.110030. https://doi.dx.org/10.1016/j.envres.2020.110030. [DOI] [PubMed] [Google Scholar]
- [90].Iqbal J, Shah NS, Sayed M, Niazi NK, Imran M, Khan JA, et al. Nano-zerovalent manganese/biochar composite for the adsorptive and oxidative removal of Congo-red dye from aqueous solutions. J Hazard Mat. 2021;403:123854. doi: 10.1016/j.jhazmat.2020.123854. https://doi.dx.org/10.1016/j.jhazmat.2020.123854. [DOI] [PubMed] [Google Scholar]
- [91].Ajayi O, Kodaolu E, Adeyemo A, Ogunsuyi H. Effects of poultry droppings on the physicochemical properties of soil and water. Nig J Soil Sci. 2003;13:50–4. [Google Scholar]
- [92].Nwachukwu M, Akinde S, Udujih O, Nwachukwu I. Effect of abattoir wastes on the population of proteolytic and lipolytic bacteria in a recipient water body (Otamiri River) Global Res J Sci. 2011;1:40–2. [Google Scholar]
- [93].Musa I, Kaltungo B. IntechOpen; London, UK: 2017. Poultry litter selection, management and utilization in the tropics. [Google Scholar]
- [94].Cavalaglio G, Coccia V, Cotana F, Gelosia M, Nicolini A, Petrozzi A. Energy from poultry waste: an aspen plus-based approach to the thermo-chemical processes. Waste Manag. 2018;73:496–503. doi: 10.1016/j.wasman.2017.05.037. https://doi.dx.org/10.1016/j.wasman.2017.05.037. [DOI] [PubMed] [Google Scholar]