Saldick J
Appl Microbiol. 1974 Dec;28(6):1004-8. doi: 10.1128/am.28.6.1004-1008.1974.
Cyanuric acid biodegrades readily under a wide variety of natural conditions, and particularly well in systems of either low or zero dissolved-oxygen level, such as anaerobic activated sludge and sewage, soils, muds, and muddy streams and river waters, as well as ordinary aerated activated sludge systems with typically low (1 to 3 ppm) dissolved-oxygen levels. Degradation also proceeds in 3.5% sodium chloride solution. Consequently, there are degradation pathways widely available for breaking down cyanuric acid discharged in domestic effluents. The overall degradation reaction is merely a hydrolysis; CO(2) and ammonia are the initial hydrolytic breakdown products. Since no net oxidation occurs during this breakdown, biodegradation of cyanuric acid exerts no primary biological oxygen demand. However, eventual nitrification of the ammonia released will exert its usual biological oxygen demand.
氰尿酸在多种自然条件下都能很容易地进行生物降解,在低溶解氧或零溶解氧水平的系统中降解效果尤其良好,比如厌氧活性污泥和污水、土壤、泥浆、泥泞的溪流和河水,以及溶解氧水平通常较低(1至3 ppm)的普通曝气活性污泥系统。在3.5%的氯化钠溶液中也会发生降解。因此,对于生活污水中排放的氰尿酸,存在广泛的降解途径。整体降解反应仅仅是水解反应;二氧化碳和氨是最初的水解分解产物。由于在这种分解过程中没有净氧化发生,氰尿酸的生物降解不会产生初级生物需氧量。然而,释放出的氨最终进行硝化作用时会产生其通常的生物需氧量。