본 연구는 염류집적 국화 재배지 토양적응성 인산분 해미생물 탐색하고 선발된 미생물 시용을 통한 염류집 적 국화 재배지 토양에서의 토양 화학성의 변화를 조 사하였으며 이를 통하여 염류 집적 국화 재배지 토양 환경 개선 기술을 개발하고자 수행되었다. 시험에 사용 된 인산분해미생물은 염류집적토양에서 분리된 Pseudomonas putida(KSJ11), Acinetobacter calcoaceticus (KSJ3) 및 Acinetobacter calcoaceticus (WP20) 3종류 이었으며 미생물의 제형은 버미큘라이트에 혼합되어 있 는 상용화된 제품을 이용하였다. 시험장소는 광주광역 시 광산구 소재 신우화훼농장의 15년간 작물이 재배되 어 염류집적현상이 나타나는 국화재배지에서 처리구 82 m2에 각각의 미생물 제재 250 L씩 시용하였다. 염 류집적이 이루어진 국화재배온실에 처리된 인산분해미 생물 Acinetobacter calcoaceticus(KSJ3; WP20)는 유 효인산을 효율적으로 분해하는 것으로 나타났으며, 특히 Acinetobacter calcoaceticus(WP20)는 염류의 분 해능력이 높았다. 인산분해미생물 시용에 따라 토양내 칼륨, 칼슘 및 마그네슘의 함량의 증가가 A. calcoaceticus(KSJ3; WP20)처리구에서 뚜렷하게 나타났 으며 이러한 변화의 영향으로 판단되는 토양내 전기전 도도도 증가되었다. 또한 인산분해미생물 시용은 선충 밀도의 감소효과를 나타내어 토양환경개선을 위한 재 료로 활용될 가능성을 나타내었다. 결과적으로 염류집 적이 이루어진 국화재배 온실에서의 인산분해미생물 시 용은 처리된 미생물의 종류에 따라 차이를 나타내었지 만 토양의 유효인산량 증가와 양이온의 유용화에는 분 명한 효과를 나타내었다. 따라서 염류집적 토양에서의 인산분해미생물 시용은 토양양분의 효율적인 사용을 가 능하게 할 수 있는 방안이 될 수 있기 때문에 시비량 절감 등의 방법으로 활용할 수 있다고 판단되었다.
This study was conducted to investigate the changes in nitrogen and soluble reactive phosphorus(SRP) contents from hanwoo manure using probiotics to feed and manure additives during 5 weeks. A total of 45 hanwoo(24 months old) with averaging 580±20 kg in weight were randomly assigned to 3 dietary treatments with 3 replicates per treatment(5 hanwoo per pen, 5 x 8 m). The treatment were supplemented, control, T1(10 kg roughage + 2 kg concentrate(2% probiotics as-fed basis)), and T2(10 kg roughage + 2 kg concentrate(2% probiotics as-fed basis) + 7 kg probiotics on the surface of hanwoo manure (top-dressing)). During the experimental period, there were statistically significant differences(P<0.05) in pH values at 3 and 5 weeks; TN contents at 5 weeks; and SRP contents at 5 weeks in all treatments. Adding probiotics to feed or feed and manure increased manure pH in comparison with controls. As time increased, changes in TN contents decreased in the order: T2 > Control > T1. Especially, the reduction in SRP contents in all treatments at 5 weeks was in following order: T1 > T2 > Control. This result suggests that it is possible to make efficient use of probiotics as feed and manure additives for reducing environmental pollution or to provide fundamental information on livestock managements to producers.
The goals of this study were conducted to investigate the effects of applying liquid aluminum chloride (AlCl3) to rice hulls on pH and soluble reactive P (SRP). A total of 800 broiler chicks (4 treatments × 4 replicates × 50 birds) were housed into 16 floor pens in a single house for 5 weeks. The treatments were divided into 4 groups: control, 100 g of liquid AlCl3/kg of rice hulls, 200 g of liquid AlCl3/kg of rice hulls, and 300 g of liquid AlCl3/kg of rice hulls. Liquid AlCl3 was sprayed on the rice hulls surface at a rate of 100 g, 200 g, and 300 g liquid AlCl3 per kg rice hull. pH values and SRP contents were significantly decreased (P<0.05) with the increased liquid AlCl3 levels in comparison with control. However, no significant differences in SRP contents were observed among all treatments at 3 and 4 weeks. Applying 100 g, 200 g, and 300 g liquid AlCl3 to rice hulls reduced SRP contents by 18, 25, and 52% for 5 weeks, respectively, compared with the controls.
In conclusion, these results suggest that using liquid AlCl3 on rice hulls should be promising for reducing water contamination and resulted in a reduction in SRP contents, which reduced pH.
The objective of this study was conducted to evaluate the effects of poultry litter amendments on pH and soluble reactive phosphorus (SRP) in poultry litter. Two laboratory studies were conducted for 42 d in Exp. 1 and for 10 d in Exp. 2, respectively. The poultry litter was treated with various amendments which included 4 g fly ash and 4 g AlCl3 (AlCl₃.6H₂O)/100 g litter in Exp. 1 and 4 g alum(Al₂(SO₄)₃.14H₂O), 8 g alum, 8.66 g liquid alum, and 17.3 g liquid alum/100 g litter in Exp. 2; untreated litter served as controls. There were no differences in pH between control and T1(4 g fly ash) and SRP contents between T1(4 g fly ash) and T2(4 g AlCl₃) in Exp. 1. A significant difference in pH and SRP contents in Exp. 2 was observed among all treatments(P< 0.05). In experiment 1, T1(4 g fly ash) and T2(4 g AlCl₃) at 42 d decreased SRP in litter by 47.1% and 62.6% of that from litter alone, repectively. In experiment 2, T1(4 g alum), T2(8.66 g liquid alum), T3(8 g alum), and T4(17.3 g liquid alum) treatments at 10 days reduced SRP contents by up to 36.2%, 62.9%, 87.0%, and 83.9%, respectively, when compared with the controls. Decrease in SRP contents was chiefly associated with reduction in litter pH. These results indicate that use of various litter amendments to limit P solubility has potential and should be pursued as a means of reducing soluble reative phosphorus during short term.