로봇 착유기의 착유컵 자동착탈을 위한 착유우의 유두위치 조사분석

권두중,김웅,이대원,Kwon, D.J.,Kim, W.,Lee, D.W. 한국축산환경학회 2002 축산시설환경학회지 Vol.8 No.3

The distance between teats of each head on twenty heads of holstein was measured in Nation Livestock Research Institute of Rural Development Administration to find design variables on the teat-cup attachment system of the auto-milking system before milking. The distance between teats was tested by the steps for milk producing in the morning and evening. The results from this study is summarized as follow. 1 The maximum and minimum length between front teats were 297mm and 112mm respectively, the maximum and minimum length between rear teats were 231mm and 36mm and the maximum and minimum length between left front and left rear were 220 and 84mm. And the maximum length of right front and right rear were 205mm and 90mm. A relative position of the each teats was asymmetric. 2. The size of teats, the length between front teats, and the length between rear teats by lactating period were very much changed for its milking. 3. The design variables on the teat-cup attachment system was found by the length between each teats tested. Since the position of teat-cup is changed by milking environment for a cow to milk, the design variables should be considered to be asymmetric area between four teat of COW.

로봇 착유기를 위한 젖소 체위측정 및 자세조정의 기초 연구

권두중,김웅,이대원,Kwon, D.J.,Kim, W.,Lee, D.W. 한국축산환경학회 2002 축산시설환경학회지 Vol.8 No.3

Physical parameters of milk cow were measured to design and build RMS(Robotic Milking System) with a tape-measurer and body parameter measurer. The parameters are very important variables to design an RMS. For the working zone space of an RMS manipulator and the movement blunting of milk cow, an interval frame was installed on the stall bottom, and then cow's behavioral reactions were tested. The results from this study is summarized as follow. 1. On the general physical condition measurement, the maximum, minimum and average body length of cow which is related to the space that the manipulator could work into the RMS were 175cm, 144cm, and 163cm respectively. It appeared that the average distance between bottom and chest was 60cm. 2. The average length between fore teats, fore and hind teats and hind teats were 178mm, 150mm and 95mm respectively. It appeared that the average length between bottom and teat attachments was 544mm, and the average length between fore teats and tail-end was 331mm. 3. Although a cow kept a some extent length between hind legs for milking, it looked a stable pose. However, the cow kept a some extent distance between front legs for milking, it looked a unstable pose. Based on results of this test, an interval frame of stall bottom should be installed around the position which was located at its hind legs.

로봇 착유기를 위한 3차원 위치정보획득 시스템

김웅,권두중,서광욱,이대원,Kim, W.,Kwon, D.J.,Seo, K.W.,Lee, D.W. 한국축산환경학회 2002 축산시설환경학회지 Vol.8 No.3

This study was carried out to measure the 3D-distance of a cow model teat for an application possibility on Robotic Milking System(RMS). A teat recognition algorithm was made to find 3D-distance of the model by using Gonzalrez's theory. Some of the results are as follows. 1 . In the distance measurement experiment on the test board, as the measured length, and the length between the center of image surface and the measured image point became longer, their error values increased. 2. The model teat was installed and measured the error value at the random position. The error value of X and Y coordinates was less than 5㎜, and that of Z coordinates was less than 20㎜. The error value increased as the distance of camera's increased. 3. The equation for distance information acquirement was satisfied with obtaining accurate distance that was necessary for a milking robot to trace teats, A teat recognition algorithm was recognized well four model cow teats. It's processing time was about 1 second. It appeared that a teat recognition algorithm could be used to determine the 3D-distance of the cow teat to develop a RMS.

홀스타인 젖소 분뇨의 특성과 비료성분 및 오염물질 부하량 추정

최동윤 ( D. Y. Choi ),최홍림 ( H. L. Choi ),곽정훈 ( J. H. Kwag ),김재환 ( J. H. Kim ),최희철 ( H. C. Choi ),권두중 ( D. J. Kwon ),강희설 ( H. S. Kang ),양창범 ( C. B. Yang ),안희권 ( H. K. Ahn ) 한국동물자원과학회 2007 한국축산학회지 Vol.49 No.1

축산물 및 가공 유기축산물 소비동향과 해결과제

김동훈 ( D. H. Kim ),성필남 ( P. N. Seong ),조수현 ( S. H. Cho ),권두중 ( D. J. Kwon ) 한국축산학회 2007 한국축산학회지 Vol.49 No.2

축분을 이용한 활성탄소 제조와 이의 악취 흡착성 분석

최희철,송준익,권두중,곽정훈,양창범,유용희,박영태,박경섭,박동금,김용국,Choi, H.C.,Song, J.I.,Kwon, D.J.,Kwag, J.H.,Yan, C.B.,Yoo, Y.H.,Park, Young-Tae,Park, K.S.,Park, D.K.,Kim, Y.K. 한국축산환경학회 2007 축산시설환경학회지 Vol.13 No.3

본 시험은 축분을 이용한 활성탄소를 제조하는 기술을 개발하고 이의 활용방안을 연구하여 축분의 처리방법을 다변화하고 제조된 활성탄소의 토양개량재, 악취흡착재 등 농업적 이용을 모색하기 위하여 악취제거시험 등을 수행하였으며 그 결과는 다음과 같다. 1. 가축분을 건조, 펠렛화 과정을 거친 후 $400^{\circ}C$에서 1시간 탄화처리하고 $750^{\circ}C$에서 1시간 활성화처리시 활성탄소가 제조되었다. 2. 축분의 회분 함량은 돈분퇴비가 11.9%로 낮았으나 계분퇴비 29.8%, 젖소깔짚 40.7%로 높았다. 휘발성물질은 젖소깔짚 11.6%, 계분퇴비 18.8%, 계분 31.0%, 돈분퇴비 22.3% 이었으나 육계깔짚은 49.8%로 높았다. 3. 축분활성탄소의 비표면적은 계분퇴비 259.8, 계분 209.8, 돈분퇴비 442.3, 젖소깔짚 $812.9\;m^2/g$으로 야자각 활성탄소 $1,040\;m^2/g$ 보다 낮았으며 미세기공의 크기는 육계깔짚 $5.02\;{\AA}$으로서 큰 반면 젖소깔짚은 $0.39\;{\AA}$으로 야자각 활성탄소와 비슷하였다. 4. 축분활성탄소의 요오드 흡착능력은 $530{\sim}580mg/g$으로 야자각 활성탄소의 1,000 mg/g 보다 낮았다. 5. 암모니아가스의 흡착율은 계분이나 계분퇴비로 만든 활성탄소가 가장 낮았으며 젖소깔짚 활성탄소가 가장 높았으며 계분퇴비 활성탄소는 20분 경에 흡착 포화에 도달하는 반면 젖소깔짚 활성탄소는 40분이 되어서 흡착 포화에 도달하였다. 6. 황화수소의 경우 휘발성물질이 비교적 많은 육계깔짚, 계분퇴비, 산란계분 등으로 만든 활성탄소에서 흡착율이 낮았으며 젖소깔짚 활성탄소에서 높았다. This study was carried out to develop the technique for manufacturing activated carbon from livestock manure and to analyse it's odor absorptiveness. Each of layer manure(LM), litter from broiler house(BL) and litter from dairy barn(DL), compost from layer manure(LC) and pig manure(PC), and coconut shell(CS) was used as a raw material. Activated carbon by grinding the raw material, adding the coal tar as a binder, palletizing, drying, heating with $N_2$ gas at $400^{\circ}C$ for 1 hour, activating by reaction with steam at a temperature of $750^{\circ}C$ for 1 hour. Moisture contents of raw material was 44.9% in layer compost, 71.9% in layer manure, 24.4% in broiler litter, 47% in pig manure compost and 33.9% in dairy litter. Volatile matter in layer compost, layer manure, broiler litter, pig manure compost and dairy litter was 18.8%, 31.0%, 49.8%, 22.3% and 11.6%, respectively. Surface area(BET) of activated carbon from layer compost, layer manure, broiler litter, pig manure compost, dairy litter and coconut shell was 259.8, 209.8, 63.5, 442.3, 812.9 and $1,040\;m^2/g$, respectively. Activated carbon made by livestock manure or litter were examined with scanning electron microscope, and micropore was a type of sponge like particles honeycombed with chambers. Pore size of activated carbon was ranged from 0.39 to $5.02\;{\AA}$, but coconut shell was $0.30\;{\AA}$. Iodine absorptiveness of activated carbon from livestock manure was $530{\sim}580mg/g$. But activated carbon made by coconut shell was 1000 mg/g. Each activated carbon could absorb odor compound very well. Absorptiveness of activated carbon from layer manure for hydrogen sulfide and trimethyl amino was 74.5% and 73.9% at the accumulated flux of 60,000 ml, but, in the case of ammonia was only 15.2% at the accumulated flux of 10,000 ml

바이오 필터를 이용한 비육돈사 배기덕트 시설의 악취저감 효과

송준익,최홍림,최희철,권두중,유용희,전중환,Song, J.I.,Choi, H.L.,Choi, H.C.,Kwon, D.J.,Yoo, Y.H.,Jeon, J.H. 한국축산환경학회 2007 축산시설환경학회지 Vol.13 No.3

무창 육성 비육돈사에 대한 악취 제어 효율 비교분석을 위하여 Biofilter 덕트에 의한 악취 제어 연구를 수행하였다. 본 실험은 서울대 부속목장 실험돈사에서 실시하였으며 실험결과는 다음과 같다. 1. 무창 육성비육돈사에서 여름철 최대 배기시 바이오필터 외부로 배출되는 공기속도는 볏짚(.0.77 m/s), ALC(0.56 m/s)으로 측정되었다. 2. 실험시작 5일 후 가스검지기(GV-100)에 의한 간이측정시 암모니아($NH_3$) 농도는 필터 통과 후 볏짚($2mg/{\ell}$), ALC(3ppm)로 측정되어 부자재 사이의 공극율이 높은 볏짚이 높게 나타났다. 부자재에 따른 필터외부에서의 먼지측정 결과 볏짚($93\;mg/m^3$), ALC($32\;mg/m^3$)으로 측정되어 볏짚은 볏짚 간의 넓은 공극에서 발생하는 먼지 및 돈사내부의 먼지가 혼합되어 필터 외부로 배출되어 돈사내부보다 높게 측정되었다. 3. 황화수소($H_{2}S$) 가스농도 변화는 돈사내부에서는 측정일 7일(6 ppm), 21일(5 ppm) 및 36일(7 ppm) 경과함에 따라 어느 일정 시점에서 황화수소 가스농도는 증가하지 않았으나 다른 필터여재에서는 일정한 경향은 보이지 않았다. 이상의 실험결과를 종합해 볼 때 무창 육성비육 돈사에서 Biofilter를 이용한 악취저감 효과를 확인할 수 있었다. Management of odors is essential to swine industry in the Republic of Korea. This study was conducted to evaluate the odor removal efficiency of biofilter ducting systems. Rice straw and auto clave concrete(ALC) were used as filter medium. The ventilation fans(5 units, diameter: 500 mm) at the side wall of a growing pig housing were connected to a biofilter using a duct. The size of a biofilter is $2.5{\times}2{\times}1.2(W{\times}L{\times}H)$. The air velocities at the 300 mm above rice straw and ALC were 0.77 and 0.56 m/s, respectively. Ammonia concentration at the outlet of rice straw and ALC media were 2 and 3 ppm, respectively. Dust concentrations were also measured. The dust concentrations of rice straw and ALC were 93, $32\;mg/m^3$, respectively. There was no significant difference between filter mediums in terms of carbon dioxide concentrations(rice straw: 320, ALC: 270 mg/l). The concentration of hydrogen sulfide was stable over the experimentation. The actual concentrations of hydrogen sulfide were 4, 3 and 3 ppm at the days of 7, 21 and 36, respectively. These results suggest that biofilter ducting systems may remove odors from pig house effectively.

변형된 사이클론 먼지포집기의 이용이 무창계사의 먼지농도에 미치는 영향

최희철,연규영,송준익,강희설,권두중,유용희,양창범,천상석,김용국,Choi, H.C.,Yeong, G.Y.,Song, J.I.,Kang, H.S.,Kwon, D.J.,Yoo, Y.H.,Yang, C.B.,Chun, S.S.,Kim, Y.K. 한국축산환경학회 2007 축산시설환경학회지 Vol.13 No.2

본 연구는 변형된 사이클론식 먼지포집기를 이용하여 계사의 먼지농도를 낮추고자 먼지포집기를 개발하였으며 무창육계사에서의 먼지 저감효과를 알아보고자 경기 화성 소재 육계농장의 무창계사에서 시험을 수행하였으며 그 결과는 다음과 같다. 1. 시험계사의 환기량은 2주령시 $0.014{\sim}0.015cmm$ 이었으며 5주령시에는 $0.158{\sim}0.181cmm$이었다. 암모니아가슬 농도는 1주령시 $13{\sim}16\;ppm$, 2주령시 $20{\sim}24ppm$이었으며 $CO_2$ 농도는 1주령시 400-500ppm이었으며 2주령 시 $1,000{\sim}2,000ppm$이었다. 2. 먼지포집기의 기계별 1주간 먼지포집량은 1주령시 104.1g, 2주령시 274.7g, 3주령시 388.6g으로 증가하다가 4주령에는 감소하였다. 3. 먼지포집기의 주령별 먼지 포집효율은 TSP의 경우 먼지포집기를 통과하기전 $3,111.7{\sim}8,745.2\;{\mu}g/m^3$로 높았으나 먼지포집기를 통과하고 난 후 $530.8{\sim}2,264.4\;{\mu}g/m^3$로 낮아져 $54.2{\sim}82.9%$의 효율을 보였으나 PM1.0의 경우 통과전 $15.2{\sim}39.0\;{\mu}g/m^3$에서 통과 후 $11.9{\sim}34.9\;{\mu}g/m^3$로 $7.6{\sim}33.8%$의 낮은 포집효율을 보였다. 4. 대조구의 경우 1주령시 TSP 농도는 $1,387.6\;{\mu}g/m^3$, 4주령시 $4,210.1\;{\mu}g/m^3$으로 높았으나 먼지포집기가 설치된 시험구의 경우 1주령시 $876.3\;{\mu}g/m^3$, 4주령시 $2,535.3\;{\mu}g/m^3$으로 $36.8{\sim}39.8%$의 먼지 저감효과가 있었다. 그러나 PM2.5, PM1.0의 경우 $11.4{\sim}39.8%$의 낮은 먼지저감 효과가 있었다. 5. 대조구의 경우 폐사율은 4.06%이었으나 시험구는 3.13%으로 낮아졌으며 출하체중도 대조구는 1.658kg인데 비하여 시험구는 1.742kg으로 높았다. This study was carried out to develop the modified cyclone dust collector in windowless broiler building measuring 12 m wide, 46 m long, with a side wall height of 3 m and a capacity of 12,800 birds. Ventilation rate in windowless broiler building was $0.014{\sim}0.015\;and\;0.158{\sim}0.181cmm$ in second weeks and fifth weeks of age, respectively. Ammonia concentration was $13{\sim}16\;and\;20{\sim}24\;ppm$ in first and second weeks of age, respectively. Amount of dust collected in dust collector each week was 104.1, 274.7 and 388.6g in first, second and third weeks of age. But it was decreased from fourth weeks of age because of the increased ventilation rate. Total suspended particulate(TSP) of polluted air was $3,111.7{\sim}8,745.2{\mu}g/m^3$, but it was decreased to $530.8{\sim}2,264.4{\mu}g/m^3$ when it passed through the dust collector. Collecting efficiency was $54.2{\sim}82.9%$ in TSP. But collecting efficiency of Particulate matter smaller than $1{\mu}g$ (PM1.0) was $7.6{\sim}33.8%$, and lower than TSP. TSP concentration in control broiler house was 1,387.6 and $4,210.1{\mu}g/m^3$ in first and fourth weeks of age, respectively. But it was decreased to 876.3 and $2,535.3{\mu}g/m^3$ in broiler house operated dust collector in first and fourth weeks of age, respectively. Dust collecting efficiency for TSP was $36.8{\sim}39.8%$, and it was decreased to $11.4{\sim}39.8%$ in smaller dust size.

Porous Calcium Silicate 및 Zeolite가 계분 유해가스 발생에 미치는 영향

전병수,최희철,김태일,권두중,노환국,강희설,김형호,한정대,최롱,박흥석,Jeon, B.S.,Choi, H.C.,Kim T.I.,Kwon, D.J.,Rho, W.G.,Kang, H.S.,Kim, H.H.,Han, J.D.,Choi, L.,Park, H.S. 한국축산환경학회 2001 축산시설환경학회지 Vol.7 No.1

In this experiment porous calcium silicate (PCS) powder prepared by using a 50 mesh sieve was spread on top of chick droppings to investigate the odor from the manure. Zeolite was used as a comparative purpose. Reduction in ammonia production from chick droppings shortly after the PCS and zeolite application was evident (P<0.05), but there were no difference among treatments afterwards. hydrogen sulfide level was significantly lowered by both PCS and zeolite treatment(P<0.05).

터널환기 무창육계사의 분진크기별 분포와 배출농도에 관한 연구

최희철,연규영,송준익,강희설,권두중,유용희,양창범,천상석,김용국,Choi, H.C.,Yeon, G.Y.,Spmg, J.I.,Kang, H.S.,Kwon, D.J.,Yoo, Y.H.,Yang, C.B.,Chun, S.S.,Kim, Y.K. 한국축산환경학회 2006 축산시설환경학회지 Vol.12 No.3

본 연구는 터널환기 무창육계사의 계사내부의 위치별 먼지 농도 분포와 배기홴에서 배출된 먼지의 확산범위를 알아보고자 수행하였으며 결과는 다음과 같다. 1. 입기구 방향의 계사 1/4 지점의 먼지농도는 TSP의 경우 $301.0{\sim}1,366.0\;{\mu}g/m^3$으로 입기구의 위치에 따라 차이가 있었다. 2. 터널홴 앞 3m 지점에서는 TSP $2065.8{\sim}3,092.2\;{\mu}g/m^3$, PM 2.5 $27.6{\sim}36.3\;{\mu}g/m^3$, PM 1.0 $8.3{\sim}11.3\;{\mu}g/m^3$으로 입기구에 비하여 증가하였다. 3. 배기홴으로부터 3m의 지점의 먼지 배출량은 TSP $354.8{\sim}574.8\;{\mu}g/m^3$으로 매우 높았으며 PM10 $94.4{\sim}156.2\;{\mu}g/m^3$, PM2.5 $14.6{\sim}18.0\;{\mu}g/m^3$, PM1.0 $6.0{\sim}6.4\;{\mu}g/m^3$ 이었다. 4. 배기홴으로부터 50m 떨어진 지점에서의 분진농도는 TSP $25.1\;{\mu}g/m^3$, PM10 $8.8\;{\mu}g/m^3$, PM2.5 $5.6\;{\mu}g/m^3$, PM1.0 $4.9\;{\mu}g/m^3$으로 매우 낮은 분진농도를 보였다. 5. 입기구와 배기구 간 분진농도의 차이는 TSP의 경우 입기구에서 $317.9\;{\mu}g/m^3$인데 비하여 배기구는 $2,678.5\;{\mu}g/m^3$로 8.42배 높았으며 PM10 7.4배, PM2.5 3.4배, PM1.0 1.6배 높았다. 6. 배기홴으로부터 거리별 분진의 배출농도는 3m 지점에서 $446.6\;{\mu}g/m^3$ 이었으나 20 m 지점에서는 $156.3\;{\mu}g/m^3$로 34.9% 수준이었고 PM10 34.9%, PM2.5 48.7%, PM1.0 86.8% 수준이었다. This study investigated the spatial distribution of dust originating from tunnel-ventilated windowless broiler building measuring 12 m wide, 61 m long, with a side wall height of 3 m and a capacity of 16,982 birds. Dust concentrations in terms of total suspended particles (TSP), and particulate matter of sizes $10\;{\mu}m$(PM10), $2.5\;{\mu}m$(PM2.5), and $1\;{\mu}m(PM1)$ were measured at 30 minutes interval by using GRIMM Aerosol Monitor (GRIMM AEROSOL). The spatial distribution of dust showed the lower dust concentration in the inlet than in the outlet of the tunnel ventilation, and dust concentration decreasing as the dust size decreased, as follows: $317.9\;{\mu}g/m^3$ TSP; $74.7{\mu}m/m^3$ PM10; $9.7\;{\mu}g/m^3$ PM2.5; and $6.2\;{\mu}g/m^3$ PM1 in the inlet; and $2,678.5\;{\mu}g/m^3$ TSP; $555.5\;{\mu}g/m^3$ PM10; $33.3\;{\mu}g/m^3$ PM2.5; and $10.2\;{\mu}g/m^3$ PM1 in the outlet. The dust concentration emitted from the tunnel ventilated fan was $446.6\;{\mu}g/m^3$ TSP; $129.1\;{\mu}g/m^3$ PM10; $15.8\;{\mu}g/m^3$ PM2.5; and $6.1\;{\mu}g/m^3$ PM1 in the 3 meters from the fan and $25.1\;{\mu}g/m^3$ TSP; $8.8\;{\mu}g/m^3$ PM10; $5.6\;{\mu}g/m^3$ PM2.5; and $4.9\;{\mu}g/m^3$ PM1 in the 50 meters from the fan.