| Keywords | 
        
            | Poultry house, Poultry fecal matter, Air pollutants | 
        
            | INTRODUCTION | 
        
            | Livestock provide essential commodities and services to the majority of the       world’s population. Demand livestock products are rapidly increasing in developing       countries due to urbanization and change in food habits, in addition       to the high nutritional needs for animal products. Indian poultry ranks 4th and       5th in world egg and broiler meat production. | 
        
            | Respectively with a total bird population of 1550 million. The combination       of intensive poultry production and certain climatic factors sometimes create       poor indoor air quality and emit air pollutants. The gases in indoor air of the       poultry house such as ammonia NH3 methane (CH4). Hydrogen sulphide (H2S).       Carbon dioxide (CO2) and oxygen (O2) are of particular importance in view of       their deleterious effect on poultry production and occupational human health.       The gases NH3, CH4 and H2S arise from the biodegradation of the accumulated fecal material under anaerobic conditions inside the poultry house. Their emissions       particularly during warm and humid conditions are high and may rise       to lethal levels due to insufficient ventilation. While O2 is essential for respiration.       CO2 is a product of respirator} metabolism. The concentrations of these       gases are directly related to bird density, type of housing, feed composition and       ventilation of the poultry house. | 
        
            | Groot Koerkamp el al. (1998) found that NH3 emissions were highest from       poultry houses as compared to those of cattle and swine. Whyte (1993) reported       that Nil; in combination with dust is the most significant respiratory       hazard to the occupational health of poultry workers. At a concentration of 15       ppm. Nil; is uncomfortable for the workers and above 50 ppm it causes injury.       While 30 ppm concentration of the gas in the poultry house affects the general       health of the birds reducing egg production and at 0.01% it produces higher       incidence of breast blisters and increased water consumption (Mac O North       1990). CH2 at concentrations above 5% is lethal to the birds besides it is also       implicated as a contributor to global warming with a potential green house       effect of about 20-30 limes that of CO2 (Duxbury et al. 1993). H2S at concentrations       above 0.05% causes death of chicken. With a pungent odor it causes irritation       of eyes/nose, headache and dizziness in humans at concentrations between       0.01- 0.05% and also causes death al 0.1% H2S when combines with       humidity in the air forms corrosive sulfuric acid and damages metal cages thus       reducing their durability. CO2 at concentrations between 0.1-0.3% O is ideal for       poultry and up to 2% is safe for human beings. The concentration of O2 usually       varies between 19- 21 percent while its concentration below 6 % is lethal for       birds as well as humans. | 
        
            | The air quality thus requires to be monitored frequently in order to ensure       safety of the birds and the workers employed in the poultry farm. Since air       quality directly reflects the sanitary and hygienic status of the poultry house its       assessment from time to time can be taken as an indicator for scheduling manure       removal operations and also for assessing the ventilation requirements. | 
        
            | MATERIALS AND METHODS | 
        
            | A cage layer open side house of dimensions 95x21 feet located at the Poultry       Eperimental Station of Acharya N.G. Ranga Agricultural University.       Rajendranagar. Hyderabad was adopted for air quality study. Half of the floor       area of the shed was taken up by droppings pit of SO cm depth. The layer house       housed 700 layer birds of 8 months age. A minimum ventilation rate of 42 cubic       meters per minute was ensured throughout the study period that lasted for 5       months. The layer house was cleared of all the fecal material before the commencement       of the study. A base line air quality data comprising concentrations       of NH3, CH4, H2S, CO2 and O2 was obtained using a gas analyzer (model-multi       gas monitor PGM-54 of Multi RAF, IR). Three measurements of each of the gas       were taken inside the poultry house at three locations 1) near to the entrance 2)       at the center and 3) at the end wall. Subsequently the air quality was assessed       once in a month in order It) study the effect of accumulation of fecal material on       the indoor air quality. The average of the values was considered for correlating       the air quality with the accumulation of the fecal matter. The total quantity of       the fresh fecal material voided by the birds per day was equal to the daily feed       consumption. The composition of the fecal matter was determined as per the | 
        
            | RESULT AND DISCUSSION | 
        
            | The birds consumed 100-110 grams feed per day the composition of which is       shown in Table 1. The quantity of the fecal material voided by the birds varied       between 2250- 2400 kg per month with the total quantity being 11.720 kg at the       end of the study period (5 months). The composition of the fecal material was as shown in Table 2. | 
        
            | Monthly air quality data from February 2005 to June 2005 is shown in Table       3. The baseline air quality of the poultry house showed absence of gases CH4,       H2S and NH3, while the concentrations of CO2 and O2, were found to be 0.17 %       and 21 % respectively. Presence of NH3, at 4 ppm concentration was detected at       the end of the February while CH4 was observed to be 0.5 % at the end of March.       H2S at a concentration of 12 was detected by the end of April. Not much variation       in the concentrations of the gases and O2 was observed, which were 0.17       and 20 % respectively. | 
        
            | Meanwhile towards the end of June 2005, concentration of NH3       increased       to 21 ppm, which was found to be causing burning sensation of eyes in workers.       Workers usually spend up to 3 hours a day in the poultry house for routine       farm operations such as feeding and egg collection. The levels of other gases       such as 1 FS and CM 14 rose to 30 ppm and 2.4%. respectively by the end of June       though the were below their deleterious levels unlike that of ammonia. Because       of the harmful effect of NH3       at 21 ppm on the workers the same was considered       to be at the maximum allowable level in the poultry house. To prevent any       further increase of NH3       , concentration the accumulated fecal matter was removed       thereby reducing harm to the poultry workers and the birds. As a result       the concentration of the gases CH4, H2S and NH3       in the indoor air of the poultry       house was brought down to zero. | 
        
            | CONCLUSIONS | 
        
            | Poultry local mailer that gets collected in the droppings pit inside the poultry       house contains high organic matter and nitrogen. As this material gets accumulated       the inner layers become anaerobic and develop reducing conditions.       Under these conditions the organic matter, unites and the sulfur present in the       fecal matter are reduced to CH4, NH4 and H2S gases. respectively. All these       gases escape into the indoor air of the poultry house and early rise in concentration       of NH3       to 21 ppm lakes place. At this concentration workers suffer due       to burning sensation of eyes and in order to avoid this the fecal mailer can be       removed when the NH3       concentration in the indoor air of the poultry house is       around 15 ppm. Thus timely removal of the fecal material based on the indoor       Nil; level avoids damage to the health of poultry workers and increases profitability       to the poultry farmer. | 
        
            | Tables at a glance | 
        
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            | References | 
        
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                AOAC, 1975. Official Methods of Analysis. Association of official analytical  chemists. I2th  Ed.Washington, D.C.
 Duxbury,  J.M., Harper, L.A and Moiser, A.R. 1993.  Contribution of agroecosystems to global  climate change. American Sociely of Agronomy.Special Publication. Madison  WI.I USA. No. 55 : 1-18.
 CirootKoerkamp,  P.W.G.. Metz. J.H.M. and Uenk, CH. 1998. Concentrations and Emissions  Ammonia in Livestock Buildings in Northern Lurope.Journal of’ Agril. Res.  ElsevierScience. 70 (1)  : 79-95.
 Mack, O.  North and Donald, D. Bell 1990. Commercial Chicken Production Manual.  Van Noslrand  Reinhold. New York. 4th Ed. 188-189.
 Whyte, R.T.1993. Aerial pollutants and the health of poultry farmers. World’s  Poutry Science Journal.49 : 139-156.
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