Lehmann H D, Marten R, Fahrner I, Gullberg C A
Artif Organs. 1981 Nov;5(4):351-6. doi: 10.1111/j.1525-1594.1981.tb04016.x.
Urea adsorption on active carbon is reversible and temperature-dependent. Urea adsorption isotherms of different carbons were determined at 0 degrees C and 65 degrees C within the equilibrium concentration range of 1.0-3.4 gm/L. At low urea concentrations considerable differences (3.4-13.0 gm/kg carbon at concentrations of 1.0 gm/L) were found between different types of activated carbon. The overall internal surface area was of minor importance compared to the pore size distribution. Adsorbing at low temperature, desorbing at high temperature, and flushing the carbon adsorber with a limited volume of the liquid to be purified yielded an "artificial urine." Compared to the original urea concentration of the filtrate, this "artificial urine" had an increased urea concentration. From a 36-liter volume containing 90 grams urea dissolved in saline, 18 liters were recirculated at a flow rate of 100 ml/min. The influence of adsorption and desorption time intervals was evaluated. After one to one and a half hours the carbon was saturated with urea. After saturation, about 1.4 grams urea were eliminated per cycle. In the "artificial urine" urea concentrations of up to 4.5 gm/L were found when the original solution contained only 2.5 gm/L. In the "patient" volume the urea concentration decreased from 2.5 gm/L to 1.9-2.1 gm/L. Within three hours a total of 22 grams of urea was removed by 3 x 120 grams activated carbon corresponding to removal of 50% of the urea passing the "artificial tubulus." The advantage of this system is that after priming, no additional physiological solution would be necessary. The necessity of excessive safety controls, additional electrolyte adjustment, energy demand in the form of direct current, and great amounts of waste in solid form lead to the conclusion that for intermittent hemofiltration treatment, commercially produced and controlled infusion solution is preferable.
尿素在活性炭上的吸附是可逆的且与温度有关。在0℃和65℃下,于1.0 - 3.4克/升的平衡浓度范围内测定了不同活性炭的尿素吸附等温线。在低尿素浓度下,不同类型的活性炭之间存在显著差异(在1.0克/升浓度时为3.4 - 13.0克/千克碳)。与孔径分布相比,总内表面积的重要性较小。在低温下吸附,在高温下解吸,并用有限体积的待净化液体冲洗碳吸附器,可得到“人工尿液”。与滤液的原始尿素浓度相比,这种“人工尿液”的尿素浓度有所增加。从含有90克溶解在盐水中的尿素的36升体积中,以100毫升/分钟的流速再循环18升。评估了吸附和解吸时间间隔的影响。一到一个半小时后,碳被尿素饱和。饱和后,每个循环约去除1.4克尿素。当原始溶液仅含2.5克/升时,在“人工尿液”中发现尿素浓度高达4.5克/升。在“患者”体积中,尿素浓度从2.5克/升降至1.9 - 2.1克/升。在三小时内,3×120克活性炭共去除了22克尿素,相当于去除了通过“人工肾小管”的尿素的50%。该系统的优点是在灌注后无需额外的生理溶液。过度的安全控制、额外的电解质调节、直流电形式的能量需求以及大量固体形式的废物,这些因素导致得出结论:对于间歇性血液滤过治疗,市售生产和控制的输液溶液更可取。