服务承诺
资金托管
原创保证
实力保障
24小时客服
使命必达
51Due提供Essay,Paper,Report,Assignment等学科作业的代写与辅导,同时涵盖Personal Statement,转学申请等留学文书代写。
51Due将让你达成学业目标
51Due将让你达成学业目标
51Due将让你达成学业目标
51Due将让你达成学业目标私人订制你的未来职场 世界名企,高端行业岗位等 在新的起点上实现更高水平的发展
积累工作经验
多元化文化交流
专业实操技能
建立人际资源圈Drug analysis
2015-06-17 来源: 51due教员组 类别: 更多范文
关于药物的作用分析
Fact Sheet Equilenin
GuidelineEquilenin is an important component in Premarin, fully synthesized in 1940 by Alfred L. Wilds., which was usually used in hormone replacement therapy. The molecular structure shows as the figure 1. The original source of steroid hormones like equilenin in driking water most likely comes from sewage treatment plants, concentrated animal feeding operations, agriculture operations and pharmaceuticals. As for its physicochemical characteristics, though equilenin itself is most hydrophobic, it can form sulfate salt and dissolve in water very well. One recent review of conjugated equine estrogens for their efficacy, safety and mechanism of action contain the information of 10 estrogens including equilenin. From their study equilenin has unique biological effects either individually or in combinations of two or three other estrogens, for the prevention of CVD and neuro-degenerative diseases like Parkinson’s disease and AD in both aging women and men. However,apart from its potent biological effects, the draw backs is also pominent. A number of observational studies suggest that the use of either equilenin alone or in combination with pro-gestin (HRT) in healthy women with aging range from 50 to 59 is associated with a increased risk of getting heart attacks.
Figure1. The molecular structure of Equilenin.
General description
Equilenin is an estrogenic steroid hormone which serves as an important component in commercial pill—Premarin used to treat women with a hysterectomy. Equilenin itself is most hydrophobic, however, it can form sulfate salt and dissolve in water very well.have well dissolve characteristics. The occurrence of pharmaceuticals, especially hormone in aquatic environment may cause a lot of problems to the health of both human and aquatic lives.
Currently, the use of pharmacological doses of premarin (5–20 μg/day in oral contraceptives , 1000 μg /day in hormone replacement therapy) to achieve positive health outcome s is both widespread and recognized as safe (Swan, 2000). However, the long-term exposure to this kind of conjugated estrogens has a potential risk of endometrial cancer based on the researches since 1975 ( Ziel H. K. et al., 1975; ANNEGERS J F, et al., 1977). And it had been proved that long-term use of estrogen would increases the possibility of getting strokes, heart attacks, blood clots and breast cancer (Brunner R L. et al., 2005). Some researchers even suggested that the increase of environmental estrogens might have a close relationship with the decline in human sex ratio recently (WHO /IPCS, 2002).
The influence of equilenin on wildlife is significant as well. Many aquatic organisms are significantly more sensitive to chemical contaminants than people, due to both level of exposure
to the chemical and differences in internal systems. Equilenin can cause the feminization of some species of male fish (Gimeno et al., 1998a, 1998b; Batty and Lim, 1999). In 2009, Tyler, C.R. has also reported that 4.2 ng/L of equilenin in the water can induce the vitellogenin in aquatic organism of oncorhynchus mykiss (Tyler C R. et al., 2009).
Receptor-binding assays measure binding of agonists or antagonists to a specific cellular receptor, which assess endocrine-disrupting activity at the molecular level of biological organization. Equilenin can specifically binds to estrogen receptor at low concentration, which has important functions in regulating important pathways for fertility and reproduction (Christen V. et al., 2010). By using sheep uterus estrogen receptors, Leusch had determined the sewage effluent of Queensland still have estrogenic activity (Leusch et al., 2005a). The steroid hormone equilenin is considered as high risk of highly active compound.
Australian significance
Many of the drugs, especially hormone drugs are designed to maintain biological activity even at very low concentration, which can be even lower than the limit of routine analytical method. (Geisy et al., 2002). Since the existence of equilenin in drinking water might threaten to public health, detecting and dealing the contamination of equilenin is very essential.
The source of steroid hormones like equilenin most likely comes from sewage treatment plants, concentrated animal feeding operations and agriculture operations (Kolodziej E P. et al., 2004) The rapidly expanding scales of synthetic hormone in pharmaceuticals contribute to the contamination of drinking water as well.
According to the data of Australian guidelines for water recycling of 2008, the maximum concentration of equilenin detected in secondary treated sewage was 280 ng/L, while the guideline value provided was only 30 ng/L (Fletcher T D. et al., 2008; Natural Resource Management Ministerial Council, Canberra, 2008) much lower than that contains in treated water. However, the recommended drinking water guideline for human pharmaceutical suggested that the maximum concentration for equilenin should not exceed 0.278 μg/L (Falconer IR et al., 2003).
Because equilenin can exert effect at very low concentration, optimizing the detection methods and treatment methods are urgent.
Treatment of drinking water
The most common treatment of recycled water among world includes secondary treatment, membrane filtration, reverse osmosis, granular activated carbon (GAC) adsorption, chlorination and ultraviolet (UV) light disinfection (Khan and Roser, 2007).At the easiest level, treatment of most wastewater is conducted by sedimentation through separation of solids from liquids. By gradually transforming dissolved material into solids, usually a biological floc, then go to a sort of of purity process. Ultraviolet light disinfection and reverse osmosis have high efficiency in dealing with steroid hormone contaminate, which can destroy more than 90% biological activity, while microfiltration or chlorination only have poor performance on the treatment of these kind of compounds (Ternes and Joss et al., 2006; Snyder et al 2007).
For steroid hormones, one of the most common degradation pathways in waters is photodegradation (Yu-Chen et al, 2005). The half-life of equilenin was 2-3 hours in river water and the degradation rate increases with the increase of pH up to 7.6 (Zhang, Y. et al., 2007). The study of reclaimed water of Queensland based on biomarker assays have shown that UV can get rid of most estrogenic activity of equilenin while the sand filter can only reduce part of it (Leusch et al., 2005).
Studies have shown that manganese dioxide (MnO2) can be used as an effective oxidative to remove most of estrogenic activity of equilenin (de Rudder. et al., 2004).
Microbial degradation of steroid hormones is another important pathway. Biodegradation of steroid hormones were prone to occur under aerobic instead of anaerobic conditions. Higher temperature can also accelerate the process of degration (Jurgens, M. D. et al., 2002).
Many studies focused on using microbacteria to deal with the water have done these years. Gram-positive bacteria like Bacillus, Nocardia, Rhodococcus, Mycobacterium, Noccardia and gram-negtive bacteria like Comamonas, Pseudomonas seem to be promising (Fujii, K. et al., 2002).
At the same time, preventive measures should apply, especially to control industrial and pharmaceutical discharges to sewerage systems.
Method of identification and detection
Equilenin can maintain estrogenic activity even at low concentration, as a result, it would be very difficult for routine analytical method to detect active equilenin in drinking water. However, LC/MS/MS is a very sensitive method and can detect samples which are at nanogram scales.
The detectiopn process shows as following. The water samples should be dechlorinated first, add surrogate standard to the sample before applying solid phase extraction. The compounds then pass through the solid phase extraction disks containing C18 functional groups and are eluted from solid phase by a small amount of methanol. Load sample to Gemini 3 μm NX-C18 HPLC column and then use LC/MS/MS for analyzing the concentration of equilenin in drinking water.
This method can detect equilenin as low as 4 ng/L within 15 minutes, and excellent linearity values can be achieved (Sueki H. Leung. et al., 2012).
Health consideration
One recent study investgated the metabolism of equilenin in MCF-7 and MDA-MB-231 human breast cancer cells. The method they use was identifing the metabolites of equilenin by GC/MS metabolite standards and deuterium-labeled analogues as internal standards. The results showed the two cell lines share the same pathways of equilenin metabolism. And the metabolism is extrahepatic, estrogen-responsive tissues. This study indicate the overwhelmingly effect of equilenin in cancer indcution. In this way, in order to avoid the bad influcence of equilenin, the warnning is that reducing the injection of such drug and make sure the water is purfied within the sate limitation.
The occurrence of steroid hormones, such as equilenin, in aquatic environment may cause a lot of problems to the health of both human and aquatic lives. Since equilenin can specifically binds to estrogen receptor, which plays an essential role in regulating important pathways for fertility and reproduction, as a consequence, detecting and dealing the contamination of equilenin is very essential, otherwise, the possibility of side effects may get higher.
References
ANZECC–ARMCANZ (Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand) (1994). Guidelines for Sewerage Systems. Acceptance of Trade Waste (Industrial Waste). Australian Water Association, Canberra
ANNEGERS J F, O’FALLON W M, DOCKERTY M B, et al. Exogenous estrogen and endometrial carcinoma: case-control and incidence study[J]. cancer, 1977, 127(572).
Batty J, Lim R. 1999. Morphological and reproductive characteristics of male mosquito fish (Gambusia affinis holbrooki) inhabiting sewage-contaminated waters in New South Wales, Australia. Arch Environ Contam Toxicol 36:301–307.
Brunner R L, Gass M, Aragaki A, et al. Effects of conjugated equine estrogen on health-related quality of life in postmenopausal women with hysterectomy: results from the Women’s Health Initiative Randomized Clinical Trial[J]. Archives of internal medicine, 2005, 165(17): 1976-1986.
Christen V, Hickmann S, Rechenberg B, et al. Highly active human pharmaceuticals in aquatic systems: a concept for their identification based on their mode of action[J]. Aquatic Toxicology, 2010, 96(3): 167-181.
Demasculinisation of sexually mature male common carp, Cyprinus carpio, exposed to 4-tert-pentylphenol during spermatogenesis. Aquat Toxicol 43:93–109.
De Rudder, J.; Van de Wiele, T.; Dhooge, W.; Comhaire, F.; Verstraete, W., Advanced water treatment with manganese oxide for the removal of 17 alphaethynylestradiol (EE2). Water Res. 2004, 38, (1), 184-192.
Falconer IR, Moore MR, Chapman HF and Ranmuthugala G. (2003). Review of Endocrine Disruptors in the context of Australian drinking water. Occasional Paper No 7. Cooperative Research Centre for Water Quality and Treatment, Salisbury, South Australia.
Fletcher T D, Deletic A, Mitchell V G, et al. Reuse of urban runoff in Australia: a review of recent advances and remaining challenges[J]. Journal of Environmental Quality, 2008, 37(5_Supplement): S-116-S-127.
Fujii, K.; Kikuchi, S.; Satomi, M.; Ushio-Sata, N.; Morita, N., Degradation of 17 beta-estradiol by a gram-negative bacterium isolated from activated sludge in a sewage treatment plant in Tokyo, Japan. Appl. Environ. Microbiol. 2002, 68, (4), 2057-2060.
Geisy JP, Hilscherova K, Jones PD, Kannan K, Machala M. 2002. Cell bioassays for detection of aryl hydrocarbon (AhR) and estrogen receptor (ER) mediated activity in environmental samples. Mar Pollut Bull 45:3–16.
Gimeno S, Komen H, Gerritsen AGM, Bowmer T. 1998a. Feminisation of young males of the common carp, Cyprinus carpio, exposed to 4-tert-pentylphenol during sexual differentiation. Aquat Toxicol 43:77–92.
Gimeno S, Komen H, Jobling S, Sumpter J, Bowmer T. 1998b.
Jurgens, M. D.; Holthaus, K. I. E.; Johnson, A. C.; Smith, J. J. L.; Hetheridge, M.; Williams, R. J., The potential for estradiol and ethinylestradiol degradation in English rivers. Environ. Toxicol. Chem. 2002, 21, (3), 480-488.
Kolodziej E P, Harter T, Sedlak D L. Dairy wastewater, aquaculture, and spawning fish as sources of steroid hormones in the aquatic environment[J]. Environmental science & technology, 2004, 38(23): 6377-6384.
Leusch FDL, Chapman HF, Ko¨rner W, Gooneratne SR, Tremblay LA. 2005a. Efficacy of an advanced biological nutrient removal plant in Queensland (Australia) to remove estrogenic chemicals. Environ Sci Technol 39:5781–5786.
Medical Research Council[J]. Natural Resource Management Ministerial Council, Canberra, 2008.
NRMMC E. AHMC, Australian guidelines for water recycling: Managing health and environmental risks (Phase 2): Augmentation of drinking water supplies, Environment Protection and Heritage Council, National Health and environment, 2008
Premarin (conjugated estrogens) Vaginal Cream - Detailed View: Safety Labeling Changes Approved By FDA Center for Drug Evaluation and Research (CDER) -- November 2008
Snyder SA, Wert EC, Hongxia (Dawn) Lei, Westeroff P and Yoon Y (2007). Removal of EDCs
and pharmaceuticals in drinking and reuse treatment processes. AWWA Research Foundation,
Denver Colorado.
Sueki H. Leung, Jenny Wei. A Fast and Effective Approach to Analyzing Hormones in Drinking Water Using SPE and LC/MS/MS[P]. Phenomenex. Inc, 2013
Swan SH. 2000. Intrauterine exposure to diethylstilbestrol: longterm effects in humans. APMIS 108:793–804.
Ternes T A, Joss A. Human pharmaceuticals, hormones and fragrances[J]. UK: IWA Publishing, 2006.
Tyler C R, Filby A L, Bickley L K, et al. Environmental health impacts of equine estrogens derived from hormone replacement therapy[J]. Environmental science & technology, 2009, 43(10): 3897-3904.
WHO/IPCS. 2002. Global assessment of the state-of-the-science of endocrine disruptors. World Health Organization/International Program on Chemical Safety. WHO/PCS/EDC/02.2. Available at: www.who.int/pcs/emerg_site/edc/global_edc_ch5. pdf
Yu-Chen, A.; Reinhard, M., Photodegradation of common environmental pharmaceuticals and estrogens in river water. Environ. Toxicol. Chem. 2005, 24, (11), 3000-3001.
Zhang, Y.; Zhou, J. L.; Ning, B., Photodegradation of estrone and 17 betaestradiol in water. Water Res. 2007, 41, (1), 19-26.
Ziel H K, Finkle W D. Increased risk of endometrial carcinoma among users of conjugated estrogens[J]. New England journal of medicine, 1975, 293(23): 1167-1170.
51Due网站原创范文除特殊说明外一切图文著作权归51Due所有;未经51Due官方授权谢绝任何用途转载或刊发于媒体。如发生侵犯著作权现象,51Due保留一切法律追诉权。

