Pharmaceutical residues, so-called “emerging” or “new” unregulated
contaminants, have raised a great deal of interest in recent years due to their
potential to cause negative effects in the environment and later in living
organisms. There is a high possibility that these compounds may be the reason
for the increase in bacterial resistance to antibiotics (D´ıaz-Cruz and
Barcelo, 2006; ´ Kim and Carlson, 2005) or disruption of the endocrine system (Vanderford
et al., 2003) causing infertility (Liu et al., 2008) and accelerated maturation
in females (Coetsier et al., 2006). Furthermore, some pharmaceuticals
(especially antidepressants and antibiotics) may be subjected to
bioaccumulation processes in aquatic organisms (mostly fish) (Chafer-Perica et
al., 2010; Jo et al., 2011). Consumption of pharmaceuticals continuously increases
and, furthermore, the introduction rate of such compounds to the environment
may exceed the degradation rate, thus in such a case they would be detected
worldwide. The exact risks associated with decades of persistent exposure to
random com binations of low levels of pharmaceuticals is not yet well
recognized (Gracia-Lor et al., 2011). Pharmaceuticals are mainly excreted in
unchanged form; however, certain compounds may be at least partially
metabolized or degraded in natural conditions to more harmful chemicals (Gros
et al., 2006b; Hanysov ˇ a´ et al., 2005) (e.g., transformation of paracetamol;
see Figure 1), thus both parent compounds and transformation products should be
of concern during analytical research. The environment is exposed to
pharmaceuticals derived from the veterinary field, medicine, and agriculture
and pharmaceuticals excreted from animals and humans (Fatta-Kassinos et al., 2011).
Moreover, additional chemicals are delivered into the environment during the
disposal of expired medications (AlOdainia et al., 2010). Many pharmaceuticals
cannot be totally removed during the treatment of drinking water (Zwiener,
2007) or during sewage treatment, thus they can be found in the effluents
(Kosjek et al., 2007) and later in the environment. In addition, livestock
excrement used as fertilizer is sprayed on farm fields, introducing
pharmaceutical residues to food and water and later to humans and animals
(Jelic et al., 2009; Kasprzyk- ´ Hordern et al., 2007). .....
2021-09-20
简要介绍 dSPE 在全自动移液工作站上应用实现全自动抗体纯化的原理。
比较了三种 Protein A 纯化 HIgG 的效率及纯化流程优化方法。
使用 IMCSTips 实验全自动纯化(一步)方法及数据分析
2021-09-20
1. IMCStips 应用原理展示
2. His-tagged 蛋白纯化流程优化及数据分析
2021-09-20
IMCStips 亲和层析柱
● 一次层析即可快速产生高纯重组蛋白
● 一致性好、回收率高,个样品的差异不到 10%
● 可结合各种复杂方法的模板化工作流
● 与 Hamilton 移液工作站结合,可在 30 分钟内处理 96 个样品
● 可定制的工作流程
2020-02-08
BenchWaver™ 把传统的平台摇摆运动与轨道振动器的圆周运动结合起来,这种最优组合能够产生最适合分子生物学应用的三维运动。
2020-02-08
强力混匀,适于细胞裂解、研磨或均质
与通用的组织研磨机更快速、更高效
采用密封2.0mL管,消除交叉感染
中通量,可同时处理3~6个样品
无锡微色谱生物科技有限公司
WuXi MicroSep Biological Science Co,. Ltd.
地 址:江苏省江阴市月城镇北环路 19 号
电 话:17715681752
工作时间:周一 ~ 周五 9:00 ~ 16:00