This review comprehensively summarizes the livestock odor reduction method by dietary manipulation, in-housing management, and manure management. The gut microbial metabolism of animals can be stimulated by low-crude protein feeding and the addition of probiotics, enzymes, plant extracts, and/or organic acids to their feed. These methods can result in reduced odor emissions from manure. For in-housing management, it is important to maintain the proper breeding density in the barn facilities, regularly remove dust and manure, and periodically clean the barn facilities. A barn using litter on the floor can reduce odor at a relatively low cost by adding adsorbents such as zeolite, biochar, etc. Although masking agent spraying can be the simplest and quickest way to control odors, it is not a fundamental odor mitigation strategy. Odor emissions can be reduced by installing covers on manure slurry storage facilities or by acidifying the manure slurry. It is necessary to install a solid-liquid separator in an enclosed facility to minimize odor emissions. Other methods for reducing odor emissions include covering manure composting plants with semi-permeable membranes or using reactor composting technology. In order to minimize odor emissions in the liquid manure composting, sufficient oxygen must be supplied during the fermentation process. Furthermore, the odor reduction effect can be achieved through the liquid manure pit recharge system which supplies matured liquid manure fertilizer to the slurry pit in the pig house.

본 연구는 돈사 내 저장된 돼지분뇨 슬러리에 액상 일라이트와 일라이트 분말을 첨가하여 악취에 미치는 영향을 분석하였다. 공시 돼지는 3원교잡종(Yorkshire×Land race×Duroc) 4개월령 암컷 비육돈 (65~68 kg) 360두를 이용하였다. 시험구 배치는 무처리한 대조구와 돼지분뇨 슬러리에 일라이트 액상 33%와 분말 5%를 첨가한 처리구로 3반복(40두) 120두에 적용하여 완전 임의배치법의 3주간 사양 시험 하였다. 악취 저감제 처리는 슬러리 피트(slurry pit ; 3.75 m×9 m×1.2 m, 20 ton 저장 규모)아래에 저장된 슬러리양을 계산하여 일정한 비율에 맞추고, 매주 액상 일라이트는 분무하거나 또는 일라이트 분말은 뿌려주었다. 악취 측정은 슬러리 피트 위 10 cm 위치에서 암모니아, 황화수소, 메틸 메르캅탄 및 디메틸 설파이드를 측정하였다. 사양기간 동안 암모니아 발생량은 일라이트 처리 형태에 의해 크게 영향을 주었다(p<0.05). 특히 암모니아 발생량은 액상 일라이트 33% 처리구는 30~46%, 일라이트 분말 5% 처리구에서는 30~54% 감소되었다. 황화수소 발생량은 2018년 12월 24일에 측정된 결과를 제외 하고 사양기간 동안 일라이트 처리 형태에 따라 유의적으로 영향을 주었다(p<0.05). 처리구의 황화수 소 발생 감소량은 대조구와 비교할 때, 액상 일라이트 33% 처리구에서는 16~60%, 일라이트 분말 5% 처리구는 7~59%였다. 측정기간 동안 평균 메틸 메르캅탄과 디메틸 설파이드 농도는 모든 시험구에서 발생되지 않았다. 3주간 사양 시험에서 평균 암모니아 농도의 경우, 액상 일라이트 33% 처리구는 38.6%, 일라이트 분말 5% 처리구는 39.7% 감소되었다(p<0.05). 평균 황화수소 농도는 액상 일라이트 33% 처리구와 일라이트 분말 5% 처리구는 비슷한 수준인 42.5% 감소되는 것으로 나타났다(p<0.05). 결론적으로 본 사양시험의 결과 액상 또는 분말 일라이트 처리는 돈사 내 발생되는 암모니아와 황화수소에 대한 유의미한 저감효과를 나타내었다.

This study was performed to measure the concentration of odorous compounds and dilution ratio values at each part of the anaerobic digester process with composting facilities using swine manure and food waste. Complex odors, ammonia, volatile fatty acids and sulfur compounds were measured at each part of the process. Complex odors measured during swine manure storage, food waste storage and in the digested liquid tank, were 35,312 Odor Unit(OU), 39,086 OU and 17,733 OU, respectively. The odor contribution index was calculated by the concentration of odorous compounds during each process divided by the threshold limit. As a result, the major odorous compound that appeared during swine manure storage, food waste storage and in the digested liquid tank was hydrogen sulfide. On the other hand, the major odorous compound in the other processes was ammonia. The overall average concentrations of ammonia were highest in the digested liquid tank(337 ppm) and the separated liquid tank(131 ppm). Wastewater treatment process(10.9 ppm) and deodorization process(11.6 ppm) revealed the lowest concentration of ammonia. The overall average concentration of total volatile fatty acids(TVFAs) was 102.8 ppb during food waste storage and among the TVFAs, the main element was propionic acid(66.1 ppb). Sulfur compounds were only detected during swine manure storage, food waste storage and in the digested liquid tank. The dominant sulfur compound was hydrogen sulfide during swine manure storage(96.3 ppm) and methyl mercaptan during food waste storage(17.7 ppm) and dimethyl sulfide during food waste storage(34.5 ppm).

We carried out basic study on the major odor substances from livestock waste treatment plant to design high efficiency offensive odor treatment facility. We choose Y and G-treatment plants and measured each samples from pre-treatment facility, water treatment facility, sludge treatment facility and offensive odor treatment facility. The odor was mainly produced from pre-treatment facility from above measurements. The concentration of hydrogen sulfide was very high as 1,200 ppm from impurity treatment facility. The concentration of hydrogen sulfide was detected as 100 ppm in waste water treatment facility(aeration facility and head) and 160∼252 ppm in sludgy treatment facility (retaining facility and scum tank). The offensive odor treatment facility was composed of washing tower using NaOCl as washing material and bio-filter. Efficiency of the offensive odor treatment facility on the hydrogen sulfide was 5∼33% and the efficiency on the ammonia was low except Y-treatment facility’s vortex mixer washing tower which is 98%. Reduction efficiency of hydrogen sulfide was increased from 14.7% to 96.3% by changing washing material, NaOH, at Y-treatment facility’s vortex mixer washing tower.

The present study investigated the emission characteristics of odorous elements from a local livestock waste treatment plant. Target materials were sampled twice from each place including the boundaries of the plant, exhaust of a fan from utility-pipe conduit and bio-filter bio-filter chamber. Among the sulfur compounds, methyl mercaptan was 3.0 ppb at the boundaryⅠ, 2.2 ppb at the fan exhaust, and 4,723.3 ppb at the outlet of bio-filter scrubber. In particular, one of main odor control facilities; bio-filter scrubber has released a large volume of methyl mercaptan. It also removes 76.8% of ammonia and 26.5% of trimethylamine.

This study was conducted to show the odor emission characteristics between the well maintained environment fundamental facility and the poorly maintained environmental facility. It also draws major components of odor emission based on facilities, stages, and suggest the proper way to reduce the level of odor for insufficient facilities. Insufficient facilities" air direct sensory and air dilution value levels are following: foodwaste ＞ livestock ＞ wastewater ＞ night-soil ＞ sewage. For the sewage and waste water facilities, the common characteristic of odor emission on each fundamental facility showed higher air dilution value in depositing reservoir and concentrator. And sulfur and aldehyde compounds came out to be the major odor causing components. In the case of night-soil and livestock facilities, the air dilution value was high in flow equalization tank and liquid erosion tank. And sulfur as well as ammonia component was the major malodorous substance. Foodwaste facility showed higher air dilution value than other facility, which sulfur and acetaldehyde compounds were acting as major malodorous substances.

This study pointed out problems on the operation by estimating process efficiency to the 3N-system(quick fermentable treatment process) which occupy plant to treat swine wastewater more than about 30 % in Jeju. And the parts to improve from problems were deduced and introduced those in situ. When the parts to improve from problems were not introduced, the Concentration of H₂S and NH₄ was 5 and 50ppm in the fermenter, respectively. But the concentration of H₂S and NH₃ was shown N.D. and 1~2 ppm in the fermenter after introduction. The concentration of H₂S and NH₃ were measured by 16 and 300 ppm highly in the aeratin tank before improvement, but those were shown N.D. and 0~1 ppm after improvement, respectively. Therefore, it showed possibility which could decrease odor efficiently with low cost by this study in 3N-system.

Odor emission effects of unit processes in 10 livestock farms and 3 manure treatment facilities in Y and I cities, Kyonggido, were simulated using puff model after the odor emission rates were measured. 2 degree level of odor intensity and 1 degree level of it were predicted by the puff model in the adjacent area of odor emission source and within the 8km radius range of it, respectively. As real time odor modelling system was operated at specific manure based fertilizer making facility located in Y city, the highest odor concentration was predicted at the entrance of that facility and relatively lower odor intensity was estimated at the place more or less be aparted from the emission sources. The higher odor intensity was evaluated at dawn and evening because the odor was accumulated in case of stable air condition.

Odor emission characteristics of unit processes in 10 livestock farms and 3 manure treatment facilities in Kyonggi province were examined in terms of odorous compound concentration and dilution ratio values of the threshold limit measured by instrumental analysis and air dilution sensory test, respectively. The highest odor concentration was detected at the compositing process unit of each facility and the dilution ratio showed high correlation with the treatment capacity as well as hygiene of the facility. Odor intensities in some facilities showed severe fluctuations (10 to 27 times difference) in response to the wind speed and direction as well as other weather conditions. According to the instrumental analysis, the major odorous compounds in the research area appeared to be ammonia, hydrogen sulfide, trimethyl amine, acetaldehyde and carbonyl compounds. Although some facilities breed same livestock, the types of odorous compounds as well as their concentration profiles were dependent on the type of composting process and management skill. In addition, dilution ratio of the threshold limit did not always show positive correlation with the odorous compound concentrations, which indicates the necessity of applying both methodologies, sensory test, and instrumental analysis.

Ulmus davidiana Nakai (UDN) has been traditionally used as a herbal medicine in Korea. In the present study, we investigated the anti-ecotoxic potential of a 116 kDa glycoprotein isolated from UDN (UDN glycoprot ein) in regulating fecal malodor and feed efficiency in mice. We found that UDN glycoprotein (200 μg/ml) has an inhibitory effect on the cell death induced by an ecotoxicological endocrine disrupting chemical, bisphenol A, in colon epithelial HT-29 cells. UDN glycoprotein did not show significant differences regarding the weight of ecotoxicity-related organs (liver, heart, kidneys, and spleen) and the levels of serum glutamate oxaloacetate transaminase, glutamate pyruvate transaminase, and lactate dehydrogenase in mice for 2 weeks, compared to the control. Additionally, UDN glycoprotein reduced the levels of hydrogen sulfide and ammonia as markers of fecal malodor in mice. Interestingly, UDN glycoprotein can improve the mouse feed efficiency. In conclusion, our data indicate that anti-ecotoxicological UDN glycoprotein has the ability to increase the feed efficiency and reduce the fecal malodor by maintaining the viability of colonic epithelial cells in mice.

It was compared the reduction effect of contaminants and odor according to DO change and EM (effective microorganisms) addition in maturation process of piggery slurry. The maturation processes were divided into three cases as follows: R-1 was operated at 2.5 mg/ℓ of DO without the addition of EM, R-2 was operated at 7.5 mg/ℓ of DO without the addition of EM and R-3 was operated at 2.5 mg/ℓ of DO with the addition of EM. The addition of EM was more effective than the increase of DO for the reduction of CODcr, NH3-N and T-N in the maturation of piggery slurry. In addition, the reducing effect of odor intensity appeared high even in the short-term maturation period in case of adding EM and one could not even smell the stimulating odor of piggery slurry.

The changes of contaminants and odor corresponding to anaerobic maturation process of piggery slurry were investigated by applying the additives, such as different kinds of complex microorganism products and deodorants containing microorganism activating agents. The pHs during 20-day anaerobic maturation were operated stably without great change regardless of the additives, although they were rather lower in the case that the additives were contained than the case that they were not contained. The effects of removing CODcr, NH3-N, T-N, and T-S in case that the additives were not contained, were not so great during the 20-day operation and so it would be difficult to remove the organic materials and nitrogen ingredients simply with anaerobic maturation process. However, in case of anaerobic maturation process that the additives were contained, their average removal rates were improved with the values of 49%, 63.5%, 48.5%, and 30.7% for above each of items, even if the 20-day of short-term maturation period was applied. Especially, odor intensity with the additives was lowered continuously during the operation period and it had more than two times of lowering effect compared to that without those.

The present study was performed to develop the removal system of the offensive gases, including hydrogen sulfide of acid gas, ammonia or amine of base gas, from the nightsoil treatment plant. In order to remove the offensive gases, the Fe-EDTA system liquid phase catalytic oxidation method with the bubble lift column reactor was employed. From the results obtained it was confirmed that the offensive gases can be deodorized simultaneously and also hydrogen sulfide of acid gas, ammonia of base gas completely removed at pH 6.45. In addition, as input gases feed rate the efficiency of acid gas did not change but the efficiency of base gases decreased to approximately 90% at pH 6.0. From the result of particle size analyzer, it was found that the particle sizes including sulfur and other impurites grew up to 21μm over 72hour reaction time.