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Emerging wastewater contaminant metformin causes intersex and reduced fecundity in fish
The occurrence of intersex fish, where male reproductive tissues show evidence of feminization, have been found in freshwater systems around the world, indicating the potential for significant endocrine disruption across species in the ecosystem. Estrogens from birth control medications in wastewater treatment plant effluent have been cited as the likely cause, but research has shown that endocrine disruption is not solely predictable based on hormone receptor interactions. Many other non-hormone pharmaceuticals are found in effluent at concentrations orders of magnitude higher than estrogens, yet there is little data indicating the impacts of these other medications. The widely prescribed anti-diabetic metformin is among the most abundant of pharmaceuticals found in effluent and is structurally dissimilar from hormones. However, we show here that exposing fathead minnows (Pimephales promelas) to a concentration of metformin found in wastewater effluent causes the development of intersex gonads in males, reduced size of treated male fish, and reduction in fecundity for treated pairs. Our results demonstrate that metformin acts as an endocrine disruptor at environmentally relevant concentrations.
Age-dependent effects in fathead minnows from the anti-diabetic drug metformin
The anti-diabetic drug metformin is thought to be the pharmaceutical most deposited into the aquatic environment by mass at up to 6 tons per year from individual WWTPs in urban areas. Recent studies have shown that exposure to 40 ug/L of metformin increased the relative expression of the egg yolk precursor protein vitellogenin in adult male fathead minnows (Pimephales promelas) (FHM). For this study, the expression of several other genes involved in estrogen biosynthesis, clearance and downstream effects were assessed in FHM after treatment to three concentrations of metformin, to better understand the estrogenic effects of metformin on FHM. In contrast to the previous study, although upward trends were observed, metformin failed to significantly alter the expression of VTG, ERα, GnRH3, and CYP3A126 in adult male FHM. However, a concentration-dependent response to metformin was observed in younger 80-90 day juvenile FHM. A 17.7-, 22-, and 22-fold increase in the relative expression of VTG mRNA in juvenile FHM exposed to 1, 10, and 100 μg/L as compared to the control was observed. There was also a 3.3-, 4.7-, and 5.5-fold increase in GnRH3 in juvenile FHM exposed to 1, 10, and 100 μg/L as compared to the control. Similarly, a 14-, 16-, and 24-fold increase in the relative expression of CYP3A126 mRNA was measured in juvenile FHM exposed to 1, 10 and 100 μg/L metformin as compared to the control. These results indicate that juvenile FHM were more susceptible to the estrogenic effects of metformin during a 7-d exposure than older, sexually mature male FHM.
Occurrence of the antidiabetic drug Metformin and its ultimate transformation product Guanylurea in several compartments of the aquatic cycle
In 2030, the World Health Organization estimates that more than 350 million people will be diagnosed with diabetes. Consequently, Metformin – the biguanide drug of choice orally administered for diabetes type II – is anticipated to see a spike in production. Unlike many pharmaceutical drugs, Metformin (Met) is not metabolized by humans but passes through the body unchanged. Entering aquatic compartments, such as in sewage, it can be bacterially transformed to the ultimate transformation product Guanylurea (Gua).
Sampling over one week (n = 5) from a Southern German sewage treatment plant revealed very high average (AV) concentrations in influent (AVMet = 111,800 ng/L, AVGua = 1300 ng/L) and effluent samples (AVMet = 4800 ng/L, AVGua = 44,000 ng/L). To provide a more complete picture of the distribution and potential persistence of these compounds in the German water cycle, a new, efficient and highly sensitive liquid chromatography mass spectrometric method with direct injection was used for the measurement of Metformin and Guanylurea in drinking, surface, sewage and seawater. Limits of quantification (LOQ) ranging from 2–10 ng/L allowed the detection of Metformin and Guanylurea in different locations such as: Lake Constance (n = 11: AVMet = 102 ng/L, AVGua = 16 ng/L), river Elbe (n = 12: AVMet = 472 ng/L, AVGua = 9 ng/L), river Weser (n = 6: AVMet = 349 ng/L, AVGua = 137 ng/L) and for the first time in marine North Sea water (n = 14: AVMet = 13 ng/L, AVGua = 11 ng/L). Based on daily water discharges, Metformin loads of 15.2 kg/d (Elbe) and 6.4 kg/d (Weser) into the North Sea were calculated. Lake Constance is used to abstract potable water which is further purified to be used as drinking water. A first screening of two tap water samples contained 2 ng/L and 61 ng/L of Metformin, respectively. The results of this study suggest that Metformin and Guanylurea could be distributed over a large fraction of the world's potable water sources and oceans. With no natural degradation processes, these compounds can be easily reintroduced to humans as they enter the food chain.
A global perspective on the use, occurrence, fate and effects of anti-diabetic drug metformin in natural and engineered ecosystems
Metformin is the most commonly used anti-diabetic drug in the world. When consumed, this unmetabolised pharmaceutical compound is excreted by the body and eventually enters the environment through a variety of pathways. Based on its high consumption and excretion rates, high concentrations of metformin have been detected in influents of wastewater treatment plants. Metformin and its transformation product, guanylurea, are also expected to be present in other aquatic environments based on their physico-chemical properties. Not surprisingly, guanylurea has also been detected in surface water, groundwater, and drinking water. Available information on ecotoxicological effects of metformin suggests that metformin is a potential endocrine disruptor and thus further emphasising the threat this drug could pose to our environment. This review provides a comprehensive overview of metformin and critically discusses available literature data with respect to its global use/demand, occurrence, fate and ecotoxicity in treatment facilities equipped with conventional and advanced treatment technologies, and its degradation/removal mechanisms. Final section highlights the existing knowledge gaps regarding its ultimate fate under the natural and engineered ecosystems and identifies some important research areas requiring urgent attention from regulatory makers and scientific community.
Metformin and Other Pharmaceuticals Widespread in Wadeable Streams of the Southeastern United States
Pharmaceutical contaminants are growing aquatic-health concerns and largely attributed to wastewater treatment facility (WWTF) discharges. Five biweekly water samples from 59 small Piedmont (United States) streams were analyzed for 108 pharmaceuticals and degradates using high-performance liquid chromatography and tandem mass spectrometry. The antidiabetic metformin was detected in 89% of samples and at 97% of sites. At least one pharmaceutical was detected at every site (median of 6, maximum of 45), and several were detected at ≥10% of sites at concentrations reported to affect multiple aquatic end points. Maximal cumulative (all detected compounds) concentrations per site ranged from 17 to 16000 ng L−1. Watershed urbanization, water table depth, soil thickness, and WWTF metrics correlated significantly with in-stream pharmaceutical contamination. Comparable pharmaceutical concentrations and detections at sites with and without permitted wastewater discharges demonstrate the importance of non-WWTF sources and the need for broad-scale mitigation. The results highlight a fundamental biochemical link between global human-health crises like diabetes and aquatic ecosystem health.
Adsorption of emerging contaminant metformin using graphene oxide
The occurrence of emerging contaminants in our water resources poses potential threats to the livings. Due to the poor treatment in wastewater management, treatment technologies are needed to effectively remove these products for living organism safety. In this study, Graphene oxide (GO) was tested for the first time for its capacity to remove a kind of emerging wastewater contaminants, metformin. The research was conducted by using a series of systematic adsorption and kinetic experiments. The results indicated that GO could rapidly and efficiently reduce the concentration of metformin, which could provide a solution in handling this problem. The uptake of metformin on the graphene oxide was strongly dependent on temperature, pH, ionic strength, and background electrolyte. The adsorption kinetic experiments revealed that almost 80% removal of metformin was achieved within 20 min for all the doses studied, corresponding to the relatively high k1 (0.232 min 1) and k2 (0.007 g mg 1 min 1) values in the kinetic models. It indicated that the highest adsorption capacity in the investigated range (qm) of GO for metformin was at pH 6.0 and 288 K. Thermodynamic study indicated that the adsorption was a spontaneous (DG0 < 0) and exothermic (DH0 < 0) process. The adsorption of metformin increased when the pH values changed from 4.0 to 6.0, and decreased adsorption were observed at pH 6.0e11.0. GO still exhibited excellent adsorption capacity after several desorption/adsorption cycles. Besides, both so-called pep interactions and hydrogen bonds might be mainly responsible for the adsorption of metformin onto GO.
originally posted by: SR1TX
I read this all, very well put together. Question I have still is this. What is the half life of such compounds? I would think that in evaporation, they would simply be broken down in the atmosphere, eaten, and destroyed?
Elsewhere, Campbell (2013) investigated the fate of nine pharmaceuticals in an anaerobic sludge digester and reported 82% mineralisation of metformin over a test period of 60 days with a calculated half-life of 26.
In a recent study, the behaviour of metformin in soils was compared with other sulfonylurea based anti-diabetic drugs (Mrozik and Stefan ska, 2014). In comparison to the other pharmaceuticals tested (glimepiride, glibencamide, gliclazide), which were much less soluble than metformin (Mrozik and Stefan ska, 2014), calculated sorption coefficient of metformin was at least one order of magnitude lower. Based on the results, it was more apparent that the soil with the highest cation exchange capacity and correspondingly the highest organic matter content had the most sorbed amount of metformin. However, the authors never mentioned if the soils were sterilised or bacterial activity sup- pressed during the sorption experiments. The same study calculated half-lives of 1-5 days for metformin under aerobic biodegradation. Thus, throughout the 24-h duration of the experiments, biodegradation is likely to have occurred and sorption may not be the only mechanism involved in metformin removal. Analysis of literature data on sorption of metformin (Mrozik and Stefan ska, 2014; Scheurer et al., 2012) as a function of organic carbon content revealed that Kd decreased as organic carbon content of soil increased (Fig. 5). In contrast an opposite trend was observed for guanylurea for same set of soils.
originally posted by: TiredofControlFreaks
a reply to: M4ngo
Just one little teensy weensy problem.
Metform affects minnows at 40 mg/L.
the concentration of metformin found in waste water is in the ng/L range.
Quite a difference there.
Taking 100 aspirin all at once will kill
Metformin showed negative impacts on the growth and devel- opment of carrots in soil concentration of 6e10 mg/kg (Eggen et al., 2011). Based on the EC50 value of metformin (64 mg/L) in the Daphnia test conducted by Cleuvers (2003), which determines the acute toxicity of a substance, this pharmaceutical compound can be classified as harmful to aquatic organisms.
Exposure of fish (fathead minnow fry) to 40 mg/L metformin for a full-life cycle beginning in early development showed impacts on repro- duction and the authors have concluded that chronic exposure to this pharmaceutical compound could potentially cause endocrine disrupting effects in fishes (Niemuth and Klaper, 2015).
Continuous high volume consumption of this compound and its release into the environment via various pathways may not show apparent acute effects but may potentially have adverse effects due to chronic exposure (Al-Odaini et al., 2010). Additionally, co- occurrence of drugs was found to have strong and positive corre- lation to wastewater effluent concentrations which may suggest synergistic effects in the environment and could potentially lead to complex ecotoxicity (Ghoshdastidar et al., 2015).
Oxidation products formed during disinfection steps could potentially be harmful to human health. DMA is an ingredient used in the synthesis of metformin hydrochloride (Shalmashi, 2008), and a major precursor of N-nitro- sodimethylamine (NDMA) which is also a probable human carcinogen (USEPA, 1993). Tukkeeree et al. (2012) reported that prepared metformin drug has been found to contain 0.0482% of DMA relative to a 500 mg metformin tablet purchased from a local pharmacy. However, even such trace levels of DMA can produce NDMA after chlorination/ozonation (Padhye et al., 2011).
It has been reported that organic precursors interact with ozone or OH to generate NDMA during water treatment (Padhye et al., 2011). Tertiary and secondary amines are dominant precursors of NDMA formation during the disinfection process (Wu et al., 2015). As such, the presence of tertiary and secondary amine moieties in the oxidation products listed in Table 6 suggests potential for NDMA formation. The active tertiary amine moiety attached to the ring structure of the identified chlorination by-product shown in Fig. 3a may also be attacked by OH or O3 and further react to form NDMA. It has been shown recently that DMA associated with branched alkyl groups or benzyl like structures having only one carbon between the ring and DMA structure consistently give higher NDMA yields (Selbes, 2014).
originally posted by: Metallicus
a reply to: M4ngo
So, what exactly are people that need Metformin to keep their sugar under control supposed to do exactly? I find this concerning because I know diabetics and they can't go without this medication.
originally posted by: TiredofControlFreaks
a reply to: M4ngo
a ng/l is 1 part per million. a mg/l is 1 part per thousand.
There is a very very big difference between those 2 numbers.
Nobody can predict how many diabetics will exist in the future and nobody can predict that metformin will still be in use by then.
Like I said - doom porn. Keep the people anxious and fearful and they will pay any amount of money to someone who can save them. Especially lucrative when there is no problem in the first place.
originally posted by: TiredofControlFreaks
a reply to: M4ngo
a ng/l is 1 part per million. a mg/l is 1 part per thousand.
There is a very very big difference between those 2 numbers.
Nobody can predict how many diabetics will exist in the future and nobody can predict that metformin will still be in use by then.
Like I said - doom porn. Keep the people anxious and fearful and they will pay any amount of money to someone who can save them. Especially lucrative when there is no problem in the first place.
Based on daily water discharges, Metformin loads of 15.2 kg/d (Elbe) and 6.4 kg/d (Weser) into the North Sea were calculated. Lake Constance is used to abstract potable water which is further purified to be used as drinking water.
originally posted by: Kettu
a reply to: Metallicus
Not a doctor, but some people claim blueberry extract works as a "natural" alternative to Metformin.
*shrug* I have no personal experience, but I know people who extol its virtues.