Siller H, Winter J
Institut für Ingenieurbiologie und Biotechnologie des Abwassers, Universität Karlsruhe.
Appl Microbiol Biotechnol. 1998 Feb;49(2):215-20. doi: 10.1007/s002530051161.
During the process of producing cassava starch from Manihot esculenta roots, large amounts of cyanoglycosides were released, which rapidly decayed to CN- following enzymatic hydrolysis. Depending on the varying cyanoglycoside content of the cassava varieties, the cyanide concentration in the wastewater was as high as 200 mg/l. To simulate anaerobic stabilization, a wastewater with a chemical oxygen demand (COD) of about 20 g/l was prepared from cassava roots and was fermented in a fixed-bed methanogenic reactor. The start-up phase for a 99% degradation of low concentrations of cyanide (10 mg/l) required about 6 months. After establishment of the biofilm, a cyanide concentration of up to 150 mg CN-/l in the fresh wastewater was degraded during anaerobic treatment at a hydraulic retention time of 3 days. All nitrogen from the degraded cyanide was converted to organic nitrogen by the biomass of the effluent. The cyanide-degrading biocoenosis of the anaerobic reactor could tolerate shock concentrations of cyanide up to 240 mg CN-/l for a short time. Up to 5 mmol/l NH4Cl (i.e. 70 mg N/l = 265 mg NH4Cl/l) in the fresh wastewater did not affect cyanide degradation. The bleaching agent sulphite, however, had a negative effect on COD and cyanide removal. For anaerobic treatment, the maximum COD space loading was 12 g l-1 day-1, equivalent to a hydraulic retention time of 1.8 days. The COD removal efficiency was around 90%. The maximum permanent cyanide space loading was 50 mg CN- l-1 day-1, with tolerable shock loadings up to 75 mg CN- l-1 day-1. Under steady-state conditions, the cyanide concentration of the effluent was lower than 0.5 mg/l.
在从木薯根生产木薯淀粉的过程中,会释放出大量氰苷,这些氰苷在酶促水解后会迅速分解为氰化物。根据木薯品种中氰苷含量的不同,废水中的氰化物浓度高达200毫克/升。为了模拟厌氧稳定化过程,用木薯根制备了化学需氧量(COD)约为20克/升的废水,并在固定床产甲烷反应器中进行发酵。低浓度氰化物(10毫克/升)99%降解的启动阶段大约需要6个月。生物膜形成后,在水力停留时间为3天的厌氧处理过程中,新鲜废水中高达150毫克CN⁻/升的氰化物浓度被降解。降解的氰化物中的所有氮都被出水生物量转化为有机氮。厌氧反应器中降解氰化物的生物群落能够在短时间内耐受高达240毫克CN⁻/升的冲击浓度。新鲜废水中高达5毫摩尔/升的氯化铵(即70毫克N/升 = 265毫克氯化铵/升)不会影响氰化物的降解。然而,漂白剂亚硫酸盐对COD和氰化物的去除有负面影响。对于厌氧处理,最大COD空间负荷为12克/升·天⁻¹,相当于水力停留时间为1.8天。COD去除效率约为90%。最大永久性氰化物空间负荷为50毫克CN⁻/升·天⁻¹,可耐受高达75毫克CN⁻/升·天⁻¹的冲击负荷。在稳态条件下,出水的氰化物浓度低于0.5毫克/升。