The content of heavy metals in face products; cosmetics and face care products.
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Barely three months into the new year and we are happy to announce a monumental milestone reached - 150 million downloads.
\n\nThis achievement solidifies IntechOpen’s place as a pioneer in Open Access publishing and the home to some of the most relevant scientific research available through Open Access.
\n\nWe are so proud to have worked with so many bright minds throughout the years who have helped us spread knowledge through the power of Open Access and we look forward to continuing to support some of the greatest thinkers of our day.
\n\nThank you for making IntechOpen your place of learning, sharing, and discovery, and here’s to 150 million more!
\n\n\n\n\n'}],latestNews:[{slug:"webinar-introduction-to-open-science-wednesday-18-may-1-pm-cest-20220518",title:"Webinar: Introduction to Open Science | Wednesday 18 May, 1 PM CEST"},{slug:"step-in-the-right-direction-intechopen-launches-a-portfolio-of-open-science-journals-20220414",title:"Step in the Right Direction: IntechOpen Launches a Portfolio of Open Science Journals"},{slug:"let-s-meet-at-london-book-fair-5-7-april-2022-olympia-london-20220321",title:"Let’s meet at London Book Fair, 5-7 April 2022, Olympia London"},{slug:"50-books-published-as-part-of-intechopen-and-knowledge-unlatched-ku-collaboration-20220316",title:"50 Books published as part of IntechOpen and Knowledge Unlatched (KU) Collaboration"},{slug:"intechopen-joins-the-united-nations-sustainable-development-goals-publishers-compact-20221702",title:"IntechOpen joins the United Nations Sustainable Development Goals Publishers Compact"},{slug:"intechopen-signs-exclusive-representation-agreement-with-lsr-libros-servicios-y-representaciones-s-a-de-c-v-20211123",title:"IntechOpen Signs Exclusive Representation Agreement with LSR Libros Servicios y Representaciones S.A. de C.V"},{slug:"intechopen-expands-partnership-with-research4life-20211110",title:"IntechOpen Expands Partnership with Research4Life"},{slug:"introducing-intechopen-book-series-a-new-publishing-format-for-oa-books-20210915",title:"Introducing IntechOpen Book Series - A New Publishing Format for OA Books"}]},book:{item:{type:"book",id:"7844",leadTitle:null,fullTitle:"Voice and Swallowing Disorders",title:"Voice and Swallowing Disorders",subtitle:null,reviewType:"peer-reviewed",abstract:"The purpose of writing this book is to discuss the updated information on voice and swallowing disorders. The book has been written by international authors and experts in this field. You will find not only clinical aspects but also basic science aspects of voice and swallowing disorders. The chapters include the quantitative analysis of activity patterns of muscles of mastication and deglutition, and salivary secretion after facial massage and vibrotactile stimulation. You will also find the updated management of oropharyngeal dysphagia, dysphagia due to cervical facial tumors, radiation-induced dysphagia, and dysphagia in patients with a stroke. This book can be an important guide to the practicing physicians and surgeons managing voice and swallowing disorders.",isbn:"978-1-83880-366-7",printIsbn:"978-1-83880-365-0",pdfIsbn:"978-1-83880-105-2",doi:"10.5772/intechopen.77662",price:119,priceEur:129,priceUsd:155,slug:"voice-and-swallowing-disorders",numberOfPages:146,isOpenForSubmission:!1,isInWos:null,isInBkci:!1,hash:"9a81e27eb29c12553e9524f20a93b57d",bookSignature:"Monjur Ahmed",publishedDate:"March 11th 2020",coverURL:"https://cdn.intechopen.com/books/images_new/7844.jpg",numberOfDownloads:5945,numberOfWosCitations:0,numberOfCrossrefCitations:0,numberOfCrossrefCitationsByBook:0,numberOfDimensionsCitations:4,numberOfDimensionsCitationsByBook:0,hasAltmetrics:1,numberOfTotalCitations:4,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"April 15th 2019",dateEndSecondStepPublish:"September 16th 2019",dateEndThirdStepPublish:"November 15th 2019",dateEndFourthStepPublish:"February 3rd 2020",dateEndFifthStepPublish:"April 3rd 2020",currentStepOfPublishingProcess:5,indexedIn:"1,2,3,4,5,6",editedByType:"Edited by",kuFlag:!1,featuredMarkup:null,editors:[{id:"206355",title:"Associate Prof.",name:"Monjur",middleName:null,surname:"Ahmed",slug:"monjur-ahmed",fullName:"Monjur Ahmed",profilePictureURL:"https://mts.intechopen.com/storage/users/206355/images/system/206355.jpeg",biography:"Monjur Ahmed, MD, FRCP, is an Associate Professor of Medicine at Thomas Jefferson University, Philadelphia, Pennsylvania, USA. He has been a practicing gastroenterologist for twenty-two years. He has a special interest in inflammatory bowel disease, eosinophilic esophagitis, gastrointestinal motility, and dysphagia. Dr. Ahmed also serves as an editor in chief for the World Journal of Gastrointestinal Oncology.",institutionString:"Thomas Jefferson University",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"8",totalChapterViews:"0",totalEditedBooks:"2",institution:{name:"Thomas Jefferson University",institutionURL:null,country:{name:"United States of America"}}}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,coeditorOne:null,coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"1098",title:"Otolaryngology",slug:"otorhinolaryngology-otolaryngology"}],chapters:[{id:"68087",title:"Quantitative Analysis of Activity Patterns in the Muscles of Mastication and Deglutition",doi:"10.5772/intechopen.88108",slug:"quantitative-analysis-of-activity-patterns-in-the-muscles-of-mastication-and-deglutition",totalDownloads:648,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"Surface electromyograms (EMGs) were recorded from the masseter (Mass), one of the major muscles for chewing, and from the suprahyoid (SH) muscles, involved in swallowing. Activity patterns of these EMGs were analyzed with a TP method that was developed specifically to quantify muscle activity patterns. To compare individual EMG bursts in a participant with different amplitudes and active durations, the bursts were cumulatively integrated to standardize the amplitudes and active durations. Each TP value calculated by this method indicated a relative location of an EMG burst on a standardized time scale free from changes in the amplitudes and active durations. Both InP and DP values were derived from the TP values and also applied to the burst. A T50 value indicated the standardized time for half of the final cumulatively integrated EMG burst. Five groups of application samples were introduced to demonstrate the usefulness of the TP method in comparing activity patterns of the Mass and SH EMGs during chewing and swallowing, while participants were in different body positions and experiencing different tastes and textures of sample foods. Finally, limitations and perspectives of the TP method are discussed.",signatures:"Yozo Miyaoka",downloadPdfUrl:"/chapter/pdf-download/68087",previewPdfUrl:"/chapter/pdf-preview/68087",authors:[null],corrections:null},{id:"68687",title:"Pathology of Nonneoplastic Lesions of the Vocal Folds",doi:"10.5772/intechopen.88735",slug:"pathology-of-nonneoplastic-lesions-of-the-vocal-folds",totalDownloads:1061,totalCrossrefCites:0,totalDimensionsCites:2,hasAltmetrics:1,abstract:"Nonneoplastic vocal fold lesions are common that can cause hoarseness and voice change. Reactive lesions of Reinke’s space can be observed in all ages and genders and comprise the majority of the benign nonneoplastic vocal fold lesions. Although clinically different terms are used to define reactive lesions of Reinke’s space, they share the same histopathologic features. In order to differentiate vocal fold polyp and nodule and Reinke’s edema, clinical findings should be considered. Epithelial changes such as pseudoepitheliomatous and verrucous hyperplasia may cause diagnostic challenge due to resemblance of squamous cell carcinoma. Evaluation of the invasion border and cellular atypia may aid in correct diagnosis.",signatures:"Nil Çomunoğlu, Şebnem Batur and Ayşe Mine Önenerk",downloadPdfUrl:"/chapter/pdf-download/68687",previewPdfUrl:"/chapter/pdf-preview/68687",authors:[null],corrections:null},{id:"68352",title:"Swallowing Disorders in Patients with Stroke",doi:"10.5772/intechopen.88341",slug:"swallowing-disorders-in-patients-with-stroke",totalDownloads:1044,totalCrossrefCites:0,totalDimensionsCites:1,hasAltmetrics:0,abstract:"Swallowing disturbance often causes by stroke and may predispose patients to malnutrition and dehydration, as well as increases the risk of such complications as suffocation and aspiration pneumonia. As an initial evaluation, the water swallowing test can be easily carried out, but not all of the aspiration can be excluded. Therefore, videofluorography (VF) and videoendoscopic examination (VE) of swallowing should be performed to find a safety method of oral intake for providing visualization of the pharynx and larynx dysfunction. Clinical severity scale is important because once the severity is determined, the treatment strategy is also known. Swallowing training can be divided into indirect training without food (basic training) and direct training with food (eating training). In general, it is important to select conditions and training diets that are easy to swallow and have a low risk of aspiration while using indirect training and direct training that aim at gradually improving the level of oral intake.",signatures:"Aiko Osawa and Shinichiro Maeshima",downloadPdfUrl:"/chapter/pdf-download/68352",previewPdfUrl:"/chapter/pdf-preview/68352",authors:[null],corrections:null},{id:"70060",title:"Maxillofacial and Oral Aspects of Dysphagia",doi:"10.5772/intechopen.89751",slug:"maxillofacial-and-oral-aspects-of-dysphagia",totalDownloads:976,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"Oral cavity/mouth is first recipient of food. Food is broken down and prepared for initial phases of digestion. The oral preparatory phase is voluntary. In this phase, food is manipulated by the tongue and teeth. A bolus which is ready to swallow is prepared. Any disruption of oral cavity functions commonly due to oral infections, space infections, facial trauma, congenital-cleft lip and palate, temporo-mandibular joint disorders, salivary gland pathology, oral cancers, radiation therapy, etc., can cause dysphagia. In this chapter, we would explain the maxillofacial and oral aspects of dysphagia along with diagnosis and treatment aspects.",signatures:"Mohammed Basha",downloadPdfUrl:"/chapter/pdf-download/70060",previewPdfUrl:"/chapter/pdf-preview/70060",authors:[null],corrections:null},{id:"69127",title:"Radiation-Related Dysphagia: From Pathophysiology to Clinical Aspects",doi:"10.5772/intechopen.88779",slug:"radiation-related-dysphagia-from-pathophysiology-to-clinical-aspects",totalDownloads:772,totalCrossrefCites:0,totalDimensionsCites:1,hasAltmetrics:0,abstract:"In Western countries, head and neck cancers (HNCs) account for about 5% of all tumors. Due to tumor locations at the aero-digestive crossroad, patients frequently suffer from swallowing dysfunction caused both by primary cancer (baseline dysphagia) and cancer therapies (treatment-related dysphagia). In this regard, radiation-induced dysphagia represents a real “Achille’s heel” which historically occurs in more than 50% of patients and can lead to a malnutritional status and an increased risk of aspiration pneumonia. In fact radiotherapy, by restricting the driving pressure of the bolus through the pharynx and/or limiting the opening of the cricopharyngeal muscle, leads to a post-swallowing pharyngeal residue that may spill into the airway causing ab ingestis pneumonia. On the contrary, an organ preservation strategy should provide both the highest tumor control probability (TCP) and the minimum function impairment with the subsequent maximum therapeutic index gain. In this regard, intensity-modulated RT (IMRT) might reduce the probability of postradiation dysphagia by producing concave dose distributions with better avoidance of several critical structures, such as swallowing organs at risk (SWOARs), which might result in better functional outcomes. Similarly, a prompt swallowing rehabilitation provided before, during, and soon after radiotherapy plays an important role in improving oncologic swallowing outcomes.",signatures:"Stefano Ursino, Paola Cocuzza, Stefania Santopadre, Fabiola Paiar and Bruno Fattori",downloadPdfUrl:"/chapter/pdf-download/69127",previewPdfUrl:"/chapter/pdf-preview/69127",authors:[null],corrections:null},{id:"68661",title:"Effect of Salivation by Facial Somatosensory Stimuli of Facial Massage and Vibrotactile Apparatus",doi:"10.5772/intechopen.88495",slug:"effect-of-salivation-by-facial-somatosensory-stimuli-of-facial-massage-and-vibrotactile-apparatus",totalDownloads:721,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"We studied the effects of salivary promotion of fluid secretion after hand massage, and the apparatus of vibrotactile stimulation (89 Hz frequency, 15 min) in normal humans. Personal massage cannot be performed on handicap and stroke patients, and then giving hand massage to them for 5 min massage gives a tired feeling. So, we focused 3 min stranger massage. Salivary glands can discharge the accumulated saliva by extrusion from the acinus glands’ massages as described in the recent Japanese textbook. We think that this method may not produce realistic recovery. Our aim ideas are to relieve stress and increase temperature with lightly touch massage of the skin and for a 1 cycle of 1 s. We recorded RR interval of ECG, total salivation, facial skin temperature, OxyHb of fNIRS on the frontal cortex, and amylase activity for the autonomic changes. In increased 2°C of the facial skin temperature, the hand massage had a need for 3 min and the vibrotactile stimulation for 15 min. Increase from 700 to 1000 ms of RR intervals had a need for 3 min in the hand massage and had 15 min in the vibrotactile stimulation. Although vibrotactile stimulation needs long time of 4–7 years as effective recovery, hand massage may have more effect with a repetition of day after day.",signatures:"Tsunoda Yumi, Akatuka Sumiko, Fukui Sayaka, Nakayama Enri, Abe Kimiko, Sato Mituyasu, Kimura Masanori, Kato Syunnichiryou, Sakai Maho, Yamaoka Masaru, Watanabe Mao, Ueda Koichirou and Hiraba Hisao",downloadPdfUrl:"/chapter/pdf-download/68661",previewPdfUrl:"/chapter/pdf-preview/68661",authors:[null],corrections:null},{id:"70540",title:"Swallowing Disorders in Cervical Facial Tumors",doi:"10.5772/intechopen.90624",slug:"swallowing-disorders-in-cervical-facial-tumors",totalDownloads:725,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"We review current state of the art protocols on swallowing disorders associated to cervical facial tumors. The clinician needs to translate physiology notions to bedside diagnosis. Facing such a case the ENT surgeon must follow several key steps: thorough history taking, barium transit, endoscopy evaluation of swallowing, high resolution diagnosis imaging. Afterwards surgical treatment plan should take into consideration the need to careful dissection of vascular and nervous structures. Dysphagia may present from initial diagnosis or after surgical resection of the tumor or during radiation and chemotherapy. We discuss the use of various staging scales or questionnaires for assessing quality of life. We illustrate the importance of swallowing disorders management with various cases of tumors at the level of skull base, pharynx, salivary glands, larynx, esophagus, etc. There are various solutions for dysphagia ranging from nasogastric feeding tube placement to percutaneous endoscopic gastrostomy to specially designed exercises. Sometimes the surgeon neglects these disorders and focuses on airway management. However, the rule should be to encourage swallowing as soon as possible after surgery. A good nutritional status is necessary for a positive prognosis in swallowing disorders. Team effort in tertiary oncology units is the key in supporting such complex cases.",signatures:"Daniela Vrinceanu and Mihai Dumitru",downloadPdfUrl:"/chapter/pdf-download/70540",previewPdfUrl:"/chapter/pdf-preview/70540",authors:[null],corrections:null}],productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"},subseries:null,tags:null},relatedBooks:[{type:"book",id:"10315",title:"Crohn’s Disease",subtitle:"Recent Advances",isOpenForSubmission:!1,hash:"1ddf7dda3ec43e99aefd9d1ac1ecc35e",slug:"crohn-s-disease-recent-advances",bookSignature:"Monjur Ahmed",coverURL:"https://cdn.intechopen.com/books/images_new/10315.jpg",editedByType:"Edited by",editors:[{id:"206355",title:"Associate Prof.",name:"Monjur",surname:"Ahmed",slug:"monjur-ahmed",fullName:"Monjur Ahmed"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"1758",title:"Otolaryngology",subtitle:null,isOpenForSubmission:!1,hash:"8b845def701f65d6ae3487686581983f",slug:"otolaryngology",bookSignature:"Balwant Singh Gendeh",coverURL:"https://cdn.intechopen.com/books/images_new/1758.jpg",editedByType:"Edited by",editors:[{id:"67669",title:null,name:"Balwant Singh",surname:"Gendeh",slug:"balwant-singh-gendeh",fullName:"Balwant Singh Gendeh"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"8732",title:"Sino-Nasal and Olfactory System Disorders",subtitle:null,isOpenForSubmission:!1,hash:"2170e4de59f7b95f9fad8d3dc343aae0",slug:"sino-nasal-and-olfactory-system-disorders",bookSignature:"Thomas Heinbockel and Balwant Singh Gendeh",coverURL:"https://cdn.intechopen.com/books/images_new/8732.jpg",editedByType:"Edited by",editors:[{id:"70569",title:"Dr.",name:"Thomas",surname:"Heinbockel",slug:"thomas-heinbockel",fullName:"Thomas Heinbockel"}],equalEditorOne:{id:"67669",title:null,name:"Balwant Singh",middleName:null,surname:"Gendeh",slug:"balwant-singh-gendeh",fullName:"Balwant Singh Gendeh",profilePictureURL:"https://mts.intechopen.com/storage/users/67669/images/system/67669.png",biography:"Dr. Balwant Singh Gendeh is a senior consultant ENT surgeon with a sub-specialty interest in rhinology (allergy, sino-nasal diseases, endoscopic sinus, anterior and ventral skull base surgery, and functional and cosmetic nasal surgery). He was an ENT registrar at the Royal Infirmary, Middlesbrough, UK, in 1993, and a JW Fulbright scholar, University of Pittsburgh, USA, in 1997. During his Fulbright experience, he also worked at the Hospital of the University of Pennsylvania (HUP), Philadelphia, USA, and St. Joseph’s Hospital, Chicago, USA, with a sub-specialty interest in rhinology and aesthetic nasal surgery. Dr. Gendeh retired after thirty-eight years of government service as a consultant ENT surgeon at the National University of Malaysia Medical Centre (UKMMC) in 2014. Currently, he is a visiting professor at the Department of Otorhinolaryngology-Head and Neck Surgery, UKMMC, and a resident ENT consultant at Pantai Hospital Kuala Lumpur. He is an executive member of numerous national and international bodies including board chairman of the Malaysian American Commission on Educational Exchange (MACEE). He was elected as a diploma of the Fellowship Academy of Medicine Malaysia (FAMM) in 2000, an international fellow of the Academy of Otolaryngology Head and Neck Surgery in 2004, a fellow of the Academy of Sciences Malaysia (FASc) in 2016, and a fellow of Malaysian Scientific Association (FMSA) in 2017. 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A cosmetic is any product that is intended to be applied superficially to the human body to keep the treated part in good health. In this process, the cosmetic should not alter the physiological functioning of the body [1]. The use of cosmetics has been practiced since antiquity as apart from cleansing, cosmetics also beautify and alter the appearance hence making the individual more appealing and attractive. There are a plethora of ingredients that were and are used in the formulation of cosmetics. The general intended purposes of cosmetics have not changed throughout centuries and millennia, the formulation of these cosmetics has undergone significant transformations, some of which include the processing and the ingredients used for their formulation. The processing has changed from a domestic/small scale production to cater for a small number of individuals to industrial/large scale production to cater for a wider consumer population with the use of worldwide advertising and social media. On the other hand, the constitution of cosmetics has also changed with time. With industrialization and the use of petrochemically-derived substances, the cosmetic formulation changed from one based on natural products to one which is mainly based on petrochemicals. However, during these past decades, there was a change in the constitution of cosmetics, to include more natural ingredients, due to the great interest and concern by consumers.
As a consequence, the massive production of cosmetic products with a wide range of ingredients, has raised several health and safety concerns. Nowadays, cosmetics are generally regulated [2]. One major concern is that cosmetics overlap in use and functionality with topical medicines. Several regulatory bodies attempted to devise a proper definition for cosmetic products with the intent to segregate cosmetic products from topical medicinal products. Within the European Union (EU), Council Directive 93/35/EEC [3] amending Council Directive 76/768/EEC, a definition for cosmetic products was laid down in article 1 of the directive. In the first part of the definition, the external body parts which may be treated with cosmetics are mentioned. Other body parts are excluded and this eludes to the understanding that cosmetic products should not be applied to these other body parts. The second part is related to the ‘activities’ which are allowed for a product to be considered as a cosmetic. These distinguish cosmetics from topical medicinal products which are intended for the control or treatment of conditions or else in making a medical diagnosis [4]. However, whereas topical medicinal products are meticulously scrutinized before their placement on the market, cosmetics do not undergo rigorous testing. Nevertheless, for cosmetic products, the manufacturers, distributors and importers are responsible for the safety of cosmetic products being placed on the market [5]. The latter regulation also states clearly what ingredients are prohibited for their presence in cosmetic products. Amongst the prohibited ingredients several heavy metals are also included. Whereas some metals and their salts are completely prohibited (e.g., tin, arsenic, cadmium, nickel and lead), other metals and their salts are either allowed with a specific limit or else only specific salts for such metals are allowed (e.g., cobalt, chromium, gold, mercury and selenium amongst others). Such additions may not be intentional as the addition of some minerals may originate from a natural source. Heavy metals, such as cadmium (Cd), lead (Pb), nickel (Ni), arsenic (As) and mercury (Hg) were also detected in numerous other raw materials which can be used for the production of cosmetics considered as natural products. These include honey [6], argan oil [7], and olive oil [8] as well as citrus essential oils [9].
Because of this, some authorities also impose limits on the presence of certain metals in cosmetics. For example, The Cosmetic Ingredient Review Expert Panel established by Food and Drug Administration (FDA) in the USA issued limits on As (5 ppm), Pb (5 ppm) and other heavy metals (20 ppm) [10]. The World Health Organisation (WHO) set limits for Pb (10 ppm), Cd (0.3 ppm) and Hg (1 ppm). The EU’s limits for Pb, Cd and chromium are 0.5, 0.5 and 1.0 ppm, respectively, while the Canadian authorities set limits for Pb (10 ppm), Cd (3 ppm) and Hg (3 ppm) [11]. However, there tends to be inconsistency in the type of metals and the limits for the metals by different authorities. As a consequence, this lack of harmonization leads to confusion amongst authorities as regulators, several manufacturers as producers and the general population as consumers. Despite all this, several researchers investigated the potential presence of heavy metals in a wide range of products. This review aims at compiling a large number of studies related to the presence of heavy metals in cosmetics and their potential harm in human beings.
Heavy metals are elements that are primarily found in the d and p-blocks of the periodic table showing a metallic character and an ability to form salts. Some sources specify that heavy metal should have a high density [12]. Such metals include lead, cadmium, nickel, mercury and arsenic amongst others.
The main concern is that heavy metals are ubiquitous and are present in several matrices both living and non-living. Particularly in living matrices, heavy metals may interfere with beneficial metals some of the latter being replaced by heavy metals that would result in the erratic physiological functioning of bodily systems. This is not an issue related only to mammals and humans, but such erratic behavior, in terms of morbidity and mortality has been observed in other animals, such as insects [13], and also in plants. Some of these heavy metals accumulate in biological systems and one source for such accumulation is the daily and/or repeated use of cosmetic products such as face powders, lipsticks and eye shadows [2]. Some heavy metals are commonly found in cosmetics [14, 15, 16, 17, 18, 19, 20].
The absorption, distribution, metabolism, excretion and interaction of heavy metals with bodily systems are complex processes that are not yet fully understood. This is even more complex when considering that some cosmetics are applied and rinsed shortly after (such as toothpastes, shampoos and conditioners and cleansers), others are applied and allowed for a few minutes to hours (such as body creams, lotions and facial makeup) and those that are applied and remain in contact with the skin for several hours (such as nail polish and hair dyes). The kinetics and dynamics of metals present in these cosmetic products, vary significantly in their fate and their extent of effects [21].
With the application of cosmetic products, the mode of entry of heavy metals in the body is via dermal or topical application. These metals may have either topical and/or systemic effects in humans [22]. At the site of application, heavy metals may accumulate in the stratum corneum causing local effects, that may be exhibited as allergic contact dermatitis associated with an excess of a metal (such as Ni, cobalt and chromium) at the site [23, 24] because of their binding to keratin [22]. In the case of Ni, this metal has a high affinity to the histidine component of the filaggrin in the stratum corneum [25]. Although, the mechanism by which heavy metals damage the skin is not yet fully understood, it is believed that this may be provoked by the formation of free radicals and/or by an inflammatory effect [26]. It was discovered that metals may accumulate with repeated application of contaminated cosmetics. Consequently, such areas would serve as reservoirs and hence lead to long-term exposure of the individual to the metal, even when such cosmetics are no longer applied [27]. The exposure of the skin to heavy metals may extend the dermal inflammation to the systemic system [26]. Ni can only penetrate and reach the general circulation, when damage is provoked by other metals [28]. Other metals such as Hg, Pb and Cd may enter the general circulation through the skin layers and transported to various organs within the body [29, 30]. This permeation can occur via sweat glands and hair follicles. Besides direct contact, oral ingestion of heavy metals may occur by the application of cosmetic products either to the lips (e.g., lipstick, lip gloss and lip balms) or within the buccal cavity (toothpastes, mouthwashes and breathe sprays) or by hand to mouth transfer of any cosmetic applied to any body part [31]. Thinner facial skin is more permeable than skin elsewhere [32]. Several studies show that certain heavy metals (such as Pb, Hg and Cd) found in topical cosmetics are found in high concentrations in the blood, urine and internal organs of individuals who use cosmetics when compared to individuals who do not [33, 34, 35, 36, 37, 38, 39, 40]. Cosmetics that are applied directly to the skin may contain moisturizing agents that increase skin permeation that may allow the entry of xenobiotics, to which some heavy metals may be bound, into the general circulation [41]. Apart from the binding of heavy metals to exogenous substances [42], these may also bind to endogenous biological molecules, hence replacing the beneficial metals. These metals may bind to several functional groups such as the amine, carboxylic and thiol function groups present in several proteins, some of which have functional roles (such as enzymes), while others have structural roles (such as collagen, keratin, actin and myosin). These metals can also bind to nucleic acids which may lead to defective DNA and RNA synthesis that may result in carcinogenesis. The application of underarm products has been hypothetically associated with the possibility of breast cancer [43]. Therefore, heavy metals provoke several toxic effects at the cellular and molecular levels [44, 45].
Several authors reported the presence of heavy metals in cosmetic products. This review gives an insight into the presence and effects of the most notorious and underestimated heavy metals in cosmetics products. The metals under discussion are lead, cadmium, nickel, mercury and arsenic.
One of the most studied heavy metals is lead. Lead is not normally used for its potential properties but it is rather considered as a contaminant with serious effects on human health. When a lead comes in contact with vital organs, it is neurotoxic, nephrotoxic and hepatotoxic [46, 47] and may provoke effects also on the reproductive system [48]. Lead can also affect fetal development through its passage via the placenta [49, 50]. Some studies have shown that it is considered a potential carcinogen to humans [51]. It has been reported that the level of Pb in the blood of consumers who use eye cosmetics was threefold higher than that of non-consumers [52]. Lead is acquired from industrial dust and fumes, car emissions, industrial chemicals such as old paints and pesticides, and a burning of fossil fuels. Food contamination may occur from some of these sources. Authorities worldwide are in a continuous struggle to establish permissible limits for Pb. The World Health Organization established a limit of 10 ppm [53]. The permissible level according to [54] is 0.1 mg/l. The FDA established a maximum permissible content of 10 ppm for Pb in color additives for the manufacture of cosmetics using Good Manufacturing Practices [10]. However, in color additives, the Pb content should not exceed 20 ppm [55]. Lead and its salts are prohibited in any cosmetic product within the EU [5]. Health Canada established a limit of 10 ppm for lead in cosmetic products [11].
As shown in Tables 1–3, several researchers investigated the presence of lead in several cosmetic products. The lipstick group is one of the most widely investigated groups with over fifteen citations. Only one study reported the absence of Pb in lipsticks [67, 70] whereas three other studies reported negligible Pb content in lipsticks [56, 57, 58] as their lower limit. Four studies showed a significantly high lead content (73.1–3760 ppm) [14, 16, 18, 57]. Most studies reported a Pb content that is within the 20 ppm permissible limit established by the FDA [59]. Some studies also tried to establish any differences between the high- and low-priced lipsticks (0.06–0.106 ppm) [60]. Eyeshadows ranks second in terms of investigated groups for Pb content. Four studies reported negligible Pb content in eyeshadows [31, 71, 72, 73] as their lower end. Whereas some studies have reported low Pb content as their lower end, the higher end exceeded the 20 ppm limit established by FDA [16, 19, 61, 71, 74]. Other eye products include eyebrow pencils (0.109–18.60 ppm) [58, 62, 63] and mascaras (ND-12.51 ppm) [58, 59, 73], all within the 20 ppm limit established by the FDA. There is only one study that reported Pb levels of 61.218 ppm in mascaras [59]. Face products vary significantly in their Pb content. Make-up foundation and face powders contain negligible Pb content up to 190 ppm as reported by [61]. Other studies did not exceed a content of 22.57 ppm [60, 63, 64], although one study reported a maximum of 41 ppm [78]. Face washes exceed the FDA limit (24.06–40.61 ppm) [14] and face creams contain minimal content of Pb (0.77 ± 1.13 ppm) [62]. Cosmetic face paint is a potential threat to frequent consumers as reported levels go up to 16.6 ppm [79]. Most hair products do not pose a potential problem as reported for hair shampoos, conditioners and dyes [17, 62, 63, 64]. Only one study reported a level of 54.56 ppm in hair products [14]. Several studies investigated body products that are applied over a larger surface area than those mentioned previously. Beauty creams contain a considerable amount of Pb with levels reaching 50.39 ppm [14, 86]. Although, somebody lotions contain low Pb levels [62], one study shows also high Pb content in such products [61]. This same study also reports a high Pb level in skin-lightening creams (up to 43.04 ppm) alongside another study showing a maximum level of 143 ppm [89]. On the other hand, two studies show low Pb contents (<4.015 ppm) [60, 64]. Cleansers and lotions also contain low Pb levels (< 22.14 ppm) [14, 62, 64]. Products that are applied to the buccal cavity include toothpaste. These may pose a problem in addition to mucosal absorption, Pb can be also ingested and absorbed via the gastrointestinal tract. In some studies, the level of Pb in toothpaste is minimal (0.036 ppm) [80], however, in other studies, the highest levels were 12.04 ppm [81] and 18.092 ppm [21].
Pb | Cd | Ni | Hg | As | |
---|---|---|---|---|---|
Lipsticks | <DL-252.4 [14, 18, 45, 56, 57, 58, 59, 60, 61, 62, 63, 64, 65, 66] 0.27–3760 [16] | ND-60.20 [14, 18, 45, 56, 58, 60, 61, 62, 63, 64, 65, 66, 67, 68, 69] | ND-22.8 [18, 45, 56, 60, 61, 62, 64, 66, 70] | <DL to 80.00 [58, 61, 62, 63] | 0.01–6.931 [58, 62, 63] |
Eye-shadows | <DL-81.5 [16, 19, 31, 58, 61, 62, 65, 71, 72, 73, 74] | <DL-55.59 [19, 58, 61, 62, 65, 71, 72, 74] | < 0.5–359.4 [19, 31, 61, 62, 71, 72, 74] | <DL-181.00 [58, 62] | <DL-1630 [58, 62, 75] |
Eyebrow pencils and eye liners | 0.109–61.22 [58, 59, 62, 63] | ND-1.12 [58, 62, 63] | 2.1–10.52 [62] | ND-67.42 [58, 62, 63] | ND-2.071 [58, 62, 63] |
Mascaras | ND-12.51 [58, 59, 73] | ND-0.034 [58] | ND-0.028 [76, 77] | ND-0.002 [58] | 0.050–1.656 [58] |
Make-up foundation | <DL to 190 [60, 61, 63, 64, 78] | <DL to 17 [45, 60, 61, 63, 64] | <DL to 13.1 [60, 61, 64] | 48.99–60.77 [63] | 0.12–1.0 [63] |
Face paints | 0.02–370 [79] | 0.01–19.2 [79] | 7.6 ppm [79] | ND-0.004 [69] | 0.125.0 [79] |
Face cream | ND-1.9 [62] | ND-0.37 [14, 62] | ND [70] | ND-1.27 [62] | ND-0.171 [62] |
Toothpaste | ND-18.092 [21, 80, 81] | ND-2.490 [80, 81, 82] | 0.025–18.535 [80, 81, 82] | ND-13.14 [81, 83] | 0.06–26.94 [83] |
The content of heavy metals in face products; cosmetics and face care products.
Pb | Cd | Ni | Hg | As | |
---|---|---|---|---|---|
Body lotions | <DL to 47.5 [61, 62] | ND [62] | ND-0.003 [62] | <DL to 47.5 [61, 62] | ND-0.007 [62] |
Hair shampoos and conditioners | 0.66–54.56 [14, 62] | ND [14, 62] | 0.01–0.06 [62] | ND-21.08 [62, 83] | 0.002–0.2 [62, 84] |
Cleansers | 0.04–22.14 [14, 62] | ND [14] | ND-0.08 [62] | ND-0.72 [62] | ND-0.009 [62] |
Lotions | 0.068–8.29 [64] | 0.007–2.13 [64] | 0.012–6.29 [64] | 18.98–19.02 [83] | 1.537–1.543 [83] |
Hair dyes and creams | 0.402–17.70 [17, 63, 64] | 0.001–1.11 [63, 64] | 0.081–4.167 [64] | 53.74–90.32 [63] | 0.16–0.71 [63] |
Tonic creams | 0.35–0.55 [85] | 0.35–0.55 [85] | 3.40–4.70 [85] | — | — |
Beauty cream | 14.38–50.39 [14, 86] | 2.40–6.27 [86] | 0.0175–5.09 [87, 88] | 47.17–124.8 [83] | 5.08–10.74 [83] |
The content of heavy metals in body products.
Pb | Cd | Ni | Hg | As | |
---|---|---|---|---|---|
Skin lightening creams | <DL-143 [21, 60, 61, 64, 89] | 0.1–1.276 [60, 64, 89] | 2.59–11.17 [60, 64] | <DL-126,000 [15, 53, 61, 70, 89, 90, 91, 92, 93, 94] | 0.7–12.30 [53, 89] |
Sunblock cream | ND-6.889 [62, 64] | ND-0.155 [62, 64] | ND-12.37 [62, 64] | ND-1.62 [62] | ND-0.01 [62] |
The content of heavy metals in face and body products.
Lead is considered as a contaminant that is present to different extents in various cosmetic preparations. Several authorities recognize Pb as a toxic metal by setting up limits for its presence in cosmetics.
Cadmium is one of the metals that has been used in cosmetics for its colored salts, ranging from deep yellow to orange [2]. It has been associated with several toxicities in humans, mainly attributed to its absorption after topical application of several cosmetics [49, 86, 95] though this is very low (0.5%). Topically, it may cause irritant dermatitis [96]. The main concern with Cd is that it tends to accumulate in human tissues and then release slowly into the general circulation. However, it normally binds to the keratin. Systemically, it mainly affects the skeletal, reproductive, metabolic [88], respiratory and renal systems [97, 98]. It has been associated with osteoporosis, diabetes, lung cancer and kidney damage [99]. It contributes also to skin ageing as it may provoke oxidative stress [25]. Despite of its presence in cosmetics, it may be found in several sources such as industrial wastes, agrochemicals (pesticides and fertilizers) and batteries. According to the WHO, the permissible limit for cadmium is 0.3 ppm [53]. The permissible level according to [54] is 0.06 mg/l. The oral limit for Cd is 0.09 μg/kg to 3 ppm as given by USP for nutritional supplements. Cadmium and its salts are prohibited in any cosmetic product within the EU [5]. Health Canada established a limit of 3 ppm for Cd in cosmetic products [11].
Cadmium is another metal, which is banned by several authorities but still found in several cosmetics, as reported by several researchers (Tables 1–3). One of the studies that reports the absence of Cd in lipsticks was conducted by [67]. Several other studies reported levels that were lower than 0.002 ppm and levels that reached content of 60.20 ppm. Despite this, only two studies showed levels of Cd higher than 5 ppm [65, 68]. Due to possible ingestion, lipstick use may be linked to systemic toxicity. A study established a difference between high-priced (0.34 ± 0.20 ppm) and low-priced (0.89 ± 0.58 ppm) lipsticks [60]. Although, eye shadows may contain the deep yellow to orange pigments more than lipsticks, the Cd content of eye shadows as reported by several researchers did not exceed 3 ppm [19, 58, 62, 63, 71, 72, 74]. However, levels of 8.89 ppm [71] and 55.59 ppm [65] were reported for eye shadows. Another eye make-up was reported to contain low Cd content by three studies. For eyebrow pencils, the maximum content of Cd was 1.12 ppm [63], whereas the content of Cd in mascaras was reported to be lower, i.e., 0.034 ppm [58]. Other facial cosmetics were also reported to contain a low amount of Cd, with levels less than 0.96 ppm [45, 60, 63, 64]. The highest level was expressed to be that of 17 ppm [61] in the make-up foundation. Similarly, Cd levels did not exceed 0.67 ppm and 0.37 ppm in face washes and face creams, respectively [14]. Tonic creams did not exceed a level of 0.55 ppm [85]. In face paints, the average level reported was 0.6 ppm [79]. Cadmium was also absent in hair shampoos and conditions, with levels being below the detection limit [14, 62]. Negligible Cd content was also present in hair dyes with levels not exceeding 1.11 ppm [63, 64]. Body cosmetics are also generally low in Cd with levels not exceeding 0.92 ppm in skin lightening creams [60, 64, 89], 0.121 ppm in sunblock creams [62, 64] and 2.13 ppm in lotions [64]. No cadmium was detected in body lotions [62] and cleansers [14]. The level of Cd in most toothpastes did not exceed 0.058 ppm [80, 81] but a maximum of 2.49 ppm was reported [82].
Although, Cd is considered one of the most common and noxious heavy metals, it seems that its use in cosmetics is very limited. It may be concluded that Cd presence in cosmetics is considered to be a contaminant rather than an ingredient, as a coloring agent.
Nickel is one of the metal impurities which is inevitably found in several natural ingredients used in cosmetic products. Most of the salts containing nickel are green in color, hence also its potential use as a colorant. However, nickel is considered to be a contact allergen that may provoke dermal sensitization, allergies, and dermatitis [100] by direct and often prolonged exposure. Persons have been diagnosed with Ni allergy due to its presence in topical cosmetic products and jewelry [101]. Nickel may also affect the respiratory system which may result in nasal and lung cancer [98]. Despite of the potential use of cosmetics to maintain the skin in a rejuvenating state, Ni in such products may lead to oxidative stress and hence promote skin aging [25]. This may be due to the overexpression of collagenases in the skin leading to the weakening of the skin matrix and a subsequent loss in elasticity [102]. The International Agency for Research on Cancer (IARC) has classified metallic Ni as a potential carcinogen to humans (Group 2B) and its compounds as carcinogenic (Group 1) [103]. Nickel may be found occurring naturally in soil and volcanic dust. This may be acquired from industrial dust and fumes. Due to the potential skin sensitization, limits for Ni presence in products have been proposed. Limits of 5 ppm [88] and 1 ppm [104] were suggested for certain household products and detergents, respectively. Likewise, in cosmetics, a Ni limit was also proposed particularly aimed for sensitized persons. Most “nickel-free” products on the market, contain less than 1 ppm of Ni [31, 105, 106]. The permissible level is 0.20 ppm according to [107] for oral consumption. Nickel and a number of its salts are prohibited in any cosmetic product within the EU [5]. These include nickel monoxide, dinickel trioxide, nickel dioxide, trinickel disulphide, tetracarbonynickel, nickel sulphide, nickel dihydroxide, nickel carbonate and nickel sulphate.
Due to its possible implications in allergenic reactions, the content of Ni in a number of cosmetic products was reported by a number of research groups (Tables 1–3). The risks associated with Ni intoxication is more possible with cosmetics that are potentially ingested. Lipsticks and lip products are amongst these candidates. Most lipstick products investigated by research groups rarely contained less than 0.20 ppm of Ni for oral consumption. Due to the short-term duration of lipstick on the lips, these products are applied frequently by consumers. This may pose a further exacerbation if ingested. The maximum levels in most studies range from 1.61 to 22.8 ppm of Ni in lipsticks [18, 45, 56, 61, 64, 66, 70]. However, in one study it was reported that the mean Ni content was 0.10 ± 0.14 ppm [62]. It was demonstrated that the price has no impact on Ni content of lipsticks (high-priced 8.24 ± 3.29 ppm and low-priced 5.15 ± 4.19 ppm) [60]. Oral consumption may be due to the accidental swallowing of toothpaste. Studies have shown the range of Ni content in most toothpaste is between 0.02 and 2.54 ppm [80, 81] but another study reported maximum levels of 18.535 ppm [82]. Dermal sensitization has been associated with eye cosmetic products. In this situation the 1 ppm threshold is applicable. Several studies have reported levels of Ni which exceed 1 ppm. Only two studies show that the minimum level of Ni in eye-shadows was less than 1 ppm [19, 31]. In several studies, maxima for Ni levels ranged between 4.133 and 359.4 ppm [61, 62, 71, 72, 74]. Nickel has been found in a green eye liner which provoked a form of contact dermatitis in a 47-year-old woman [76] whereas another study reported contact allergy to a Ni-containing mascara [77]. A study reported a mean Ni content of 6.31 ± 4.21 ppm in eyebrow pencils [62]. Most make-up foundation products seem to contain high amounts of Ni, quoting the minimum values above 3 ppm and the maximum values to 13.01 ppm [60, 64]. Only one study reported values being less than the detection limit [61]. In a study on face paints, the average Ni content was 7.6 ppm [79]. However, in other facial formulations such as face washes and creams, the content was reported to be very low with a mean of 0.04 ± 0.11 ppm [14] or not detectable [70] for these formulations respectively. Hair products are of no major concern, as the levels in shampoos and conditions do not exceed 0.06 ppm whereas the highest content of Ni in hair dyes is 4.167 ppm [64]. Body products vary in Ni content. In general, Ni does not exceed 12.37 ppm, but the 1 ppm of Ni is exceeded for most products that include skin lightening creams, sun blocks, tonic creams and body creams [60, 64, 85, 87, 88]. Body lotions and cleansers seem to contain very low Ni contents (<0.08 ppm) [62].
Whereas Ni in mascaras and eye shadows has been implicated in its involvement in allergic chronic dermatitis, several studies have reported that Ni allergy cannot be considered as the main risk factor in patients reporting eye-lid dermatitis [108].
Mercury is one of the heavy metals that is widely used in cosmetic formulations. Although, mercury is known as a shiny, silvery, dense liquid, it may occur in various inorganic and organic compounds. In the inorganic form, such as ammoniated Hg, it is used for its skin lightening properties, whereas in the organic form, such as phenyl mercuric and ethyl mercuric salts, it is used as a preservative in mascaras and eye makeup cleansing products [90, 109]. After dermal application, Hg penetrates through the skin via the hair follicles and sweat glands [29, 96]. During this process, part of the Hg is reduced to the metallic form that accumulates in the skin tissue. Hg blocks tyrosinase in situ, inhibiting the melanin-forming enzyme [110], hence its use in skin-lightening creams [22]. Only one study mentioned that cream had the abbreviation ‘precip blanc’ on the label, which should suggest that this product contains Hg [36]. Systemically, Hg may exhibit a range of signs which include vomiting, nausea and kidney damage, central nervous sytstem effect which include irritability, tremors, weakness, nervousness, fatigue and memory loss. It may affect also the sensorial systems, that is, loss in hearing, taste and vision. Finally, high Hg content may lead to death [111, 112]. In some instances, following dermal absorption and systemic uptake, Hg may induce autoimmune glomerulonephritis. Studies reveal significant accumulation of mercury in several organs and body fluids, such as hair (22.5 ppm, twice that in non-cosmetic users), blood (up to 233 nmol/l, more than four times than that in non-cosmetic users] and urine (up to 2531 nmol/day, fifty times more than that in non-cosmetic users) [39, 91, 113, 114].
Mercury is a metallic element that is naturally occurring in the environment and its compounds are the most common form that exists naturally in the environment. Due to its ubiquity, several authorities issued limitations for Hg use. For instance, the FDA restricts its use and is regulated in cosmetic products. The FDA allows a maximum level of 1 ppm of Hg in mercury-contaminated lead acetate when used as a colour in cosmetics [10]. Within the European Union, mercury and its compounds are not allowed in cosmetics, whereas phenyl mercuric salts are only allowed as preservatives in eye care products at a maximum allowable level of 70 ppm [5] whereas in the US it is allowed up to a level of 65 ppm by weight [10]. Health Canada allows a maximum Hg content of 1 ppm in cosmetics [11].
The main emphasis of analysis by researchers was conducted on skin-lightening creams due to their interaction with melanin metabolism. Very few studies report levels below the 3 ppm threshold [15, 53, 70] (Tables 1–3). Other studies reveal values up to 126,000 ppm [61, 89, 90, 91, 92, 93]. Although, in some lipstick products, the Hg content was below the detection limit [58, 61, 62], some of these same studies and others reveal contents up to 80 ppm [63]. The status of Hg contamination in eye cosmetic products varies significantly with levels of up to 181 pm in eye shadows [58, 62], 67.42 ppm in eyebrow pencils [58, 62, 63] but levels of up to 0.002 ppm in mascaras [58]. Apart from the make-up foundation where levels of Hg reach a maximum level of 60.77 ppm [63], other face products contain minimal amounts of Hg, such as face creams (0.09 ± 0.37 ppm [62]), sunblock creams (0.41 ± 1.21 ppm [62]) and face paints (<0.004 ppm [69]). In some studies, it was reported that the content of Hg in hair products is below the detection limit [62] whereas in other studies, it reached a maximum of 90.32 ppm [63, 83]. Body care products such as body lotions and cleansers contain varied amounts of Hg [62], with products from the first group with contents up to 47.5 ppm [61]. In some beauty creams, the Hg level reached a maximum of 124.8 ppm [83]. The presence of mercury in toothpaste has not been widely investigated, but in two studies, the Hg level was reported to reach a maximum of 13.14 ppm [81, 83].
As can be concluded from these studies, Hg is one of the least detected heavy metals in most cosmetics [22], but not in skin-lightening products. Mercury is found intentionally in face and skin care products rather than in products for purely cosmetic use. Apart from skin-lightening properties, Hg compounds are claimed to reduce and remove freckles, treat acne, and prevent and remove wrinkles [22].
Arsenic is a metalloid that is present ubiquitously as a major contaminant in the environment. Although, it is redox inactive, its target functional groups are sulfydryl groups on proteins which may lead to the depletion of glutathione [115], an essential antioxidant of an amino acid origin, which prevents damage of cellular components caused by radicals and heavy metals. On long-term dermal exposure, As can cause hyperpigmentation and keratosis
In general, several studies reveal that As is not a significant contaminant and levels of this metalloid rarely exceed the 3 ppm limit (Tables 1–3). In lipsticks, although most studies report a level of up to 0.34 ppm [62, 63], a study reported a maximum level of 6.931 ppm of As [58]. In eye cosmetics, the maximum permissible limit is rarely exceeded. In general, eye shadows, eyebrow pencils and mascaras do not contain As levels more than 3.704, 2.071 and 1.656 ppm, respectively [58, 62, 63]. However, in a study, it was reported that in kohl, there was an alarming presence of As (810–1630 ppm). Kohl is an ancient eye cosmetic still used nowadays [75]. The danger with kohl is not solely because of its use as a cosmetic but there are claims that falsely indicating its use for the treatment of eye conditions. Apart from the presence of As in kohl, other face cosmetics, such as foundations and creams contain minimal quantities of As, reported as up to 1.0 and 0.171 ppm, respectively [62, 63]. Less commonly used products include face paints particularly used by opera actors in China. Levels of As reach a maximum of 25 ppm [79]. Shampoos, conditioners and dyes used on the hair contain low As concentrations (<0.71 ppm) [62, 63, 94]. Likewise, in a study, the As content for cleansers and sunblocks does not exceed 0.010 ppm [62] but higher levels were reported for body lotions (1.543 ppm) [83]. There are some concerns with skin-lightening creams as some exceed the 3 ppm threshold [53, 89] and other creams with levels up to 10.74 ppm [83]. In some toothpaste, the As content was 26.94 ppm [83]. Most likely, As is present as a contaminant with other heavy metals used for this purpose. In spite of these findings, As is one of those elements that is rarely found in cosmetics [22]. However, its presence may raise concerns particularly in legal products that are used on a long-term basis and in illegal cosmetic products on the underground market.
The studies discussed in the previous sections highlight the importance of specific metals as contaminants and additives in cosmetic products. To determine any particular relationships between formulations, a multi-variate meta-analysis was carried out using Spearman correlation and Principal Component Analysis, taking into account the maximum levels obtained for the various cosmetic formulations. Pearson correlation statistics (Table 4) reveal a relationship between all five metals (r > 0.466). Two latent factors had an eigenvalue greater than 1, which together explained 80.54% of the total variance. The factor loadings demonstrated the different groups of variables (Figure 1). Factor 1, displayed on the horizontal axis, weighed heavily on Pb, Cd, Ni and As with lipsticks, eye shadows, face paints, make-up foundation and skin lightening creams exhibiting high levels of these metals. These formulations were discriminately different from the rest. On the other hand, F2, displayed on the vertical axis, weighed heavily on Hg with skin lightening creams having superior quantities of this metal for the other formulations. This multi-variate analysis consolidates the findings from previous studies. The findings of such research works are at the disposition of authorities and policy makers for the formulation of high-quality cosmetic products.
Variables | Cd | Ni | Hg | As |
---|---|---|---|---|
Pb | 0.538 | 0.495 | 0.527 | 0.579 |
Cd | 0.779 | 0.334 | 0.750 | |
Ni | 0.446 | 0.641 | ||
Hg | 0.465 |
Spearman correlation matrix for the five metals.
Observations plot for the formulations. Legend: Lp = lipsticks; Es = eye shadows; Ep = eyepencils; Ma = mascaras; Mf = foundation; Fp = face paint; Fc = face cream; Tp = toothpaste; SLc = skin-lightening creams; Sb = sunblock; Hp = hair products; Hd = hair dyes; Bl = body lotion; Cl = cleansers; Lo = lotions; and Tc = tonic creams.
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All published Book Chapters are licensed under a Creative Commons Attribution 3.0 Unported License. Monographs are licensed under the Creative Commons Attribution-NonCommercial 4.0 International (CC BY-NC 4.0) license granted to all others. Our Copyright Policy aims to guarantee that original material is published while at the same time giving significant freedom to our Authors. IntechOpen upholds a flexible Copyright Policy meaning that there is no copyright transfer to the publisher and Authors hold exclusive copyright to their work.
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\n\n\n\nIntechOpen is committed to disseminating high-quality scientific research in a manner that exemplifies the best practice in scholarly publishing. IntechOpen is an official member of the Committee on Publication Ethics (COPE), which advocates the maintenance of the highest ethical standards for all parties involved in the act of publishing, including Authors, Academic Editors of the book, Peer Reviewers, the publisher and Societies, where applicable.
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Marine eutrophication has a negative impact on food security, ecosystem health and economy through disruptions in tourism, fisheries and health industries. Both N and P have known point and non-point sources. Control of point sources has been easier than non-point sources particularly agricultural sources for both N and P as well as fossil fuel combustion for N, which remains a major challenge. Implementing mitigation strategies for N has been reported to be effective for P mitigation; however, the converse is not true due to mobility and volatility of N. Excessive N and P cause algae blooms, anoxic conditions, and ocean acidification with these conditions leading to dead zones, fish kill, toxin production, altered plant species diversity, food web disruption, tourism disruption and health issues. 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Increasing concerns about pollution levels in the oceans and coastal regions have led to multiple approaches for measuring and mitigating marine pollution, in order to achieve sustainable marine water quality. Satellite remote sensing, covering large and remote areas, is considered useful for detecting and monitoring marine pollution. Recent developments in sensor technologies have transformed remote sensing into an effective means of monitoring marine areas. Different remote sensing platforms and sensors have their own capabilities for mapping and monitoring water pollution of different types, characteristics, and concentrations. This chapter will discuss and elaborate the merits and limitations of these remote sensing techniques for mapping oil pollutants, suspended solid concentrations, algal blooms, and floating plastic waste in marine waters.",book:{id:"7547",slug:"monitoring-of-marine-pollution",title:"Monitoring of Marine Pollution",fullTitle:"Monitoring of Marine Pollution"},signatures:"Sidrah Hafeez, Man Sing Wong, Sawaid Abbas, Coco Y. T. Kwok,\nJanet Nichol, Kwon Ho Lee, Danling Tang and Lilian Pun",authors:[{id:"225316",title:"Dr.",name:"Sawaid",middleName:null,surname:"Abbas",slug:"sawaid-abbas",fullName:"Sawaid Abbas"},{id:"259861",title:"Ms.",name:"Sidrah",middleName:null,surname:"Hafeez",slug:"sidrah-hafeez",fullName:"Sidrah Hafeez"},{id:"259890",title:"Prof.",name:"Man Sing",middleName:null,surname:"Wong",slug:"man-sing-wong",fullName:"Man Sing Wong"}]},{id:"35057",doi:"10.5772/33720",title:"Surface Water Quality Monitoring in Nigeria: Situational Analysis and Future Management Strategy",slug:"surface-water-quality-monitoring-in-nigeria-situational-analysis-and-future-management-strategy",totalDownloads:13239,totalCrossrefCites:13,totalDimensionsCites:25,abstract:null,book:{id:"1998",slug:"water-quality-monitoring-and-assessment",title:"Water Quality",fullTitle:"Water Quality Monitoring and Assessment"},signatures:"A.M. Taiwo, O.O. Olujimi, O. Bamgbose and T.A. Arowolo",authors:[{id:"96826",title:"Prof.",name:"Toyin",middleName:null,surname:"Arowolo",slug:"toyin-arowolo",fullName:"Toyin Arowolo"},{id:"138905",title:"Mr.",name:"Adewale Mathew",middleName:null,surname:"Taiwo",slug:"adewale-mathew-taiwo",fullName:"Adewale Mathew Taiwo"},{id:"138908",title:"Mr.",name:"Olanrewaju Olusoji",middleName:null,surname:"Olujimi",slug:"olanrewaju-olusoji-olujimi",fullName:"Olanrewaju Olusoji Olujimi"},{id:"138915",title:"Prof.",name:"Olukayode",middleName:null,surname:"Bamgbose",slug:"olukayode-bamgbose",fullName:"Olukayode Bamgbose"}]},{id:"17390",doi:"10.5772/17734",title:"Spatial Interpolation Methodologies in Urban Air Pollution Modeling: Application for the Greater Area of Metropolitan Athens, Greece",slug:"spatial-interpolation-methodologies-in-urban-air-pollution-modeling-application-for-the-greater-area",totalDownloads:3516,totalCrossrefCites:11,totalDimensionsCites:24,abstract:null,book:{id:"193",slug:"advanced-air-pollution",title:"Advanced Air Pollution",fullTitle:"Advanced Air Pollution"},signatures:"Despina Deligiorgi and Kostas Philippopoulos",authors:[{id:"29291",title:"Prof.",name:"Despina",middleName:null,surname:"Deligiorgi",slug:"despina-deligiorgi",fullName:"Despina Deligiorgi"},{id:"38634",title:"MSc.",name:"Kostas",middleName:null,surname:"Philippopoulos",slug:"kostas-philippopoulos",fullName:"Kostas Philippopoulos"}]}],mostDownloadedChaptersLast30Days:[{id:"64603",title:"Detection and Monitoring of Marine Pollution Using Remote Sensing Technologies",slug:"detection-and-monitoring-of-marine-pollution-using-remote-sensing-technologies",totalDownloads:4450,totalCrossrefCites:15,totalDimensionsCites:29,abstract:"Recently, the marine habitat has been under pollution threat, which impacts many human activities as well as human life. Increasing concerns about pollution levels in the oceans and coastal regions have led to multiple approaches for measuring and mitigating marine pollution, in order to achieve sustainable marine water quality. Satellite remote sensing, covering large and remote areas, is considered useful for detecting and monitoring marine pollution. Recent developments in sensor technologies have transformed remote sensing into an effective means of monitoring marine areas. Different remote sensing platforms and sensors have their own capabilities for mapping and monitoring water pollution of different types, characteristics, and concentrations. This chapter will discuss and elaborate the merits and limitations of these remote sensing techniques for mapping oil pollutants, suspended solid concentrations, algal blooms, and floating plastic waste in marine waters.",book:{id:"7547",slug:"monitoring-of-marine-pollution",title:"Monitoring of Marine Pollution",fullTitle:"Monitoring of Marine Pollution"},signatures:"Sidrah Hafeez, Man Sing Wong, Sawaid Abbas, Coco Y. T. Kwok,\nJanet Nichol, Kwon Ho Lee, Danling Tang and Lilian Pun",authors:[{id:"225316",title:"Dr.",name:"Sawaid",middleName:null,surname:"Abbas",slug:"sawaid-abbas",fullName:"Sawaid Abbas"},{id:"259861",title:"Ms.",name:"Sidrah",middleName:null,surname:"Hafeez",slug:"sidrah-hafeez",fullName:"Sidrah Hafeez"},{id:"259890",title:"Prof.",name:"Man Sing",middleName:null,surname:"Wong",slug:"man-sing-wong",fullName:"Man Sing Wong"}]},{id:"52206",title:"Particulate Matter Sampling Techniques and Data Modelling Methods",slug:"particulate-matter-sampling-techniques-and-data-modelling-methods",totalDownloads:3411,totalCrossrefCites:5,totalDimensionsCites:12,abstract:"Particulate matter with 10 μm or less in diameter (PM10) is known to have adverse effects on human health and the environment. For countries committed to reducing PM10 emissions, it is essential to have models that accurately estimate and predict PM10 concentrations for reporting and monitoring purposes. In this chapter, a broad overview of recent empirical statistical and machine learning techniques for modelling PM10 is presented. This includes the instrumentation used to measure particulate matter, data preprocessing, the selection of explanatory variables and modelling methods. Key features of some PM10 prediction models developed in the last 10 years are described, and current work modelling and predicting PM10 trends in New Zealand—a remote country of islands in the South Pacific Ocean—are examined. In conclusion, the issues and challenges faced when modelling PM10 are discussed and suggestions for future avenues of investigation, which could improve the precision of PM10 prediction and estimation models are presented.",book:{id:"5356",slug:"air-quality-measurement-and-modeling",title:"Air Quality",fullTitle:"Air Quality - Measurement and Modeling"},signatures:"Jacqueline Whalley and Sara Zandi",authors:[{id:"188593",title:"Associate Prof.",name:"Jacqueline",middleName:null,surname:"Whalley",slug:"jacqueline-whalley",fullName:"Jacqueline Whalley"},{id:"188594",title:"Ms.",name:"Sara",middleName:null,surname:"Zandi",slug:"sara-zandi",fullName:"Sara Zandi"}]},{id:"72766",title:"Industrial Air Emission Pollution: Potential Sources and Sustainable Mitigation",slug:"industrial-air-emission-pollution-potential-sources-and-sustainable-mitigation",totalDownloads:883,totalCrossrefCites:2,totalDimensionsCites:4,abstract:"Air of cities especially in the developing parts of the world is turning into a serious environmental interest. The air pollution is because of a complex interaction of dispersion and emission of toxic pollutants from manufactories. Air pollution caused due to the introduction of dust particles, gases, and smoke into the atmosphere exceeds the air quality levels. Air pollutants are the precursor of photochemical smog and acid rain that causes the asthmatic problems leading into serious illness of lung cancer, depletes the stratospheric ozone, and contributes in global warming. In the present industrial economy era, air pollution is an unavoidable product that cannot be completely removed but stern actions can reduce it. Pollution can be reduced through collective as well as individual contributions. There are multiple sources of air pollution, which are industries, fossil fuels, agro waste, and vehicular emissions. Industrial processes upgradation, energy efficiency, agricultural waste burning control, and fuel conversion are important aspects to reducing pollutants which create the industrial air pollution. Mitigations are necessary to reduce the threat of air pollution using the various applicable technologies like CO2 sequestering, industrial energy efficiency, improving the combustion processes of the vehicular engines, and reducing the gas production from agriculture cultivations.",book:{id:"10178",slug:"environmental-emissions",title:"Environmental Emissions",fullTitle:"Environmental Emissions"},signatures:"Rabia Munsif, Muhammad Zubair, Ayesha Aziz and Muhammad Nadeem Zafar",authors:[{id:"251787",title:"Dr.",name:"Muhammad",middleName:null,surname:"Zubair",slug:"muhammad-zubair",fullName:"Muhammad Zubair"},{id:"318519",title:"Ms.",name:"Rabia",middleName:"Jathol",surname:"Munsif",slug:"rabia-munsif",fullName:"Rabia Munsif"},{id:"320637",title:"Ms.",name:"Ayesha",middleName:null,surname:"Aziz",slug:"ayesha-aziz",fullName:"Ayesha Aziz"},{id:"320675",title:"Dr.",name:"Muhammad Nadeem",middleName:null,surname:"Zafar",slug:"muhammad-nadeem-zafar",fullName:"Muhammad Nadeem Zafar"}]},{id:"48090",title:"Biological Contamination of Air in Indoor Spaces",slug:"biological-contamination-of-air-in-indoor-spaces",totalDownloads:2727,totalCrossrefCites:5,totalDimensionsCites:8,abstract:null,book:{id:"4572",slug:"current-air-quality-issues",title:"Current Air Quality Issues",fullTitle:"Current Air Quality Issues"},signatures:"Anca Maria Moldoveanu",authors:[{id:"25924",title:"Prof.",name:"Anca",middleName:"Maria",surname:"Moldoveanu",slug:"anca-moldoveanu",fullName:"Anca Moldoveanu"}]},{id:"64537",title:"Degradation Pathways of Persistent Organic Pollutants (POPs) in the Environment",slug:"degradation-pathways-of-persistent-organic-pollutants-pops-in-the-environment",totalDownloads:2020,totalCrossrefCites:8,totalDimensionsCites:19,abstract:"Persistent organic pollutants (POPs) are resistant to most of the known environmental degradation processes. Because of their persistence, POPs bioaccumulate in animal tissues and biomagnify along food chains and food webs with potential adverse impacts on human and wildlife health and the environment. Although POPs are resistant to most of the environmental degradation processes, there are some environmental processes mostly microbial degradation that can degrade POPs to other forms that are not necessarily simpler and less toxic. The Stockholm Convention on Persistent Organic Pollutants adopted in 2001 was meant to restrict the production and use of these toxic chemicals in the environment.",book:{id:"7224",slug:"persistent-organic-pollutants",title:"Persistent Organic Pollutants",fullTitle:"Persistent Organic Pollutants"},signatures:"James T. Zacharia",authors:[{id:"28551",title:"Dr.",name:"James T.",middleName:null,surname:"Zacharia",slug:"james-t.-zacharia",fullName:"James T. Zacharia"}]}],onlineFirstChaptersFilter:{topicId:"133",limit:6,offset:0},onlineFirstChaptersCollection:[{id:"81825",title:"Quantification of Heavy Metal Levels in Sediments of the “Palizada” River in a Protected Natural Area of Southeastern Mexico",slug:"quantification-of-heavy-metal-levels-in-sediments-of-the-palizada-river-in-a-protected-natural-area-",totalDownloads:5,totalDimensionsCites:0,doi:"10.5772/intechopen.104657",abstract:"This chapter shows the results of the determination of the levels of Copper (Cu), Iron (Fe), Magnesium (Mg), Manganese (Mn), and Cadmium (Cd) in sediments of the “Palizada River”; evaluated by atomic absorption. The results show high levels of Fe, Mg, and Mn concerning previous studies and are directly related to agricultural and livestock activities in the area. The metal-metal correlation analysis show significant values, suggesting that the generation source is the same. Some of the pollutants produced by industrial or population centers; end up in natural water bodies; by different physical processes, such as precipitation, complex formation, and others. These contaminants can bioaccumulate in aquatic organisms and reach humans through the food chain. Certain heavy metals such as cadmium (Cd) produced by human activities have been found in the oceans and the tissues of different organisms; which constitutes a risk for consumption; Cd is classified as an element that predisposes to the presence of Cancer. Therefore, the study of sediments is fundamental for determining the degree of contamination of an ecosystem.",book:{id:"11120",title:"Environmental Impact and Remediation of Heavy Metals",coverURL:"https://cdn.intechopen.com/books/images_new/11120.jpg"},signatures:"Carlos Montalvo, Claudia A. Aguilar, Yunuen Canedo, Alejandro Ruiz, Brenda Zermeño, Ruby S. Gines and Rosa M. Cerón"},{id:"81354",title:"Concentration Levels of Heavy Metals and Selected Ions in the Irrigation Water: The Case of Little Akaki River, Addis Ababa, Ethiopia",slug:"concentration-levels-of-heavy-metals-and-selected-ions-in-the-irrigation-water-the-case-of-little-ak",totalDownloads:22,totalDimensionsCites:0,doi:"10.5772/intechopen.103677",abstract:"Irrigable water resources have been challenged by the contamination of heavy metals and unwanted ions that impair plant growth and human health. It impaired the quality of edible fruit & vegetables. The objective of this study was to determine the concentration of heavy metals (Pb, Cd, Cr, and Cu) and selected ions (chloride, Na, Mg, Ca), and to evaluate its suitability for irrigation use. Water samples were collected from three various locations (the upstream, middle stream, and downstream) of the river. Temperature (T), EC, pH, and total dissolved solids (TDS) were tested onsite using handheld multiparameter testing equipment, while the heavy metals (Pb, Cd, Cr, and Cu) and selected ions (Chloride, Na, Mg, and Ca) of the water sample were analyzed using (ICP-OES). ANOVA test was conducted to examine the concentration variations of heavy metals and selected ions between the sampling locations along the river. The concentrations of (Pb and Cd) were found (2.5–3.9), (0.03–0.4) mg/L respectively, and (Cr and Cu) were below the detectible limit of the (ICP-OES) equipment. Cadmium (Cd) was found to be higher than the permissible limit of FAO (0.01mg/L) for irrigation water. There was no significant variation of heavy metals and selected ions between the sampling locations.",book:{id:"11120",title:"Environmental Impact and Remediation of Heavy Metals",coverURL:"https://cdn.intechopen.com/books/images_new/11120.jpg"},signatures:"Mekonnen M. Tarekegn and Getaneh L. Weldekidan"},{id:"81083",title:"Heavy Metal’s Environmental Impact",slug:"heavy-metal-s-environmental-impact",totalDownloads:32,totalDimensionsCites:0,doi:"10.5772/intechopen.103907",abstract:"Heavy metals are inorganic elements with something like a density of more than 5 g/cm3. Essential and non-essential heavy metals were divided into two groups based on their toxicity. Heavy metals, unlike organic pollutants, are non-biodegradable and tend to accumulate in living things. Many heavy metal ions are hazardous or carcinogenic. The majority of heavy metals, such as cadmium, copper, and zinc, are linked to pollution and hazardous concerns. There are more than 50 elements categorized as heavy metals, with 17 of them being extremely hazardous and easily accessible. Metal pollutants are often non-degradable and have no recognized homeostasis mechanism. Their mere presence in aquatic habitats is enough to have a direct or indirect impact on living systems. The anthropogenic pollution of heavy metals in ancient mining regions refers to areas where the concentration of one or more heavy metals exceeds normal values. Heavy metals disrupt cellular organelles and components in biological systems. Nanoscale zero-valent iron is a promising alternative for heavy metal cleanup. Heavy metal ions are poisonous, non-degradable, and tend to bioaccumulate and biomagnify. The purpose of this chapter is to display some heavy metals and the environmental impact of these minerals, which includes soil, plants, and humans.",book:{id:"11120",title:"Environmental Impact and Remediation of Heavy Metals",coverURL:"https://cdn.intechopen.com/books/images_new/11120.jpg"},signatures:"Riyam N. Khalef, Amal I. Hassan and Hosam M. Saleh"},{id:"80885",title:"Distribution of Potentially toxic elements in Water, Sediment and Soils in the Riparian Zones around a Kraft Pulp and Paper Mill in Western Kenya",slug:"distribution-of-potentially-toxic-elements-in-water-sediment-and-soils-in-the-riparian-zones-around-",totalDownloads:30,totalDimensionsCites:0,doi:"10.5772/intechopen.102440",abstract:"This chapter discusses the impact of effluent discharge on the distribution of potentially toxic elements (Pb, Cd, Cu and Zn) in water, sediments and soils near a Kraft mill in Western Kenya. Potentially Toxic Elements (PTEs) concentrations were determined at three sites: Water Intake Point, Effluent Discharge Point and Downstream Point. The mill liquid effluent parameters and gaseous emissions were also characterized. One-way ANOVA was used to analyze the spatial differences in PTEs concentrations. Principal component analysis determined the correlations between the proximity to the Kraft mill and the PTEs in soils, water and sediments. In riverine soils, Cd was 0.78 ± 0.01 mg/kg, while Pb was 94.38 ± 9.65 mg/kg. In sediments, the concentration was 16.81 ± 2.46 mg/kg for Zn, 6.16 ± 0.72 mg/kg for Cd and 75.28 ± 5.97 mg/kg for Pb. In water, Zn was 0.26 ± 0.038 mg/L, Cu was 0.75 ± 0.11 mg/L, Cd was 0.05 ± 0.004 mg/L and Pb was 1.26 ± 9.65 mg/L. The spatial distributions of PTEs in soils near the factory and across the river may have resulted from the factory’s effluent discharge and gaseous emissions. These findings should help formulate more stringent industrial effluent management programs in Western Kenya.",book:{id:"11120",title:"Environmental Impact and Remediation of Heavy Metals",coverURL:"https://cdn.intechopen.com/books/images_new/11120.jpg"},signatures:"Elijah S. Omutange, Julius O. Manyala, Anne N. Wekesa, Odipo Osano, Thomas Munyao, Alfred A. Otieno and Lazare Etiégni"},{id:"80488",title:"Phytoextraction of Zn(II) and Cu(II) by Canna indica: Related Physiological Effects",slug:"phytoextraction-of-zn-ii-and-cu-ii-by-canna-indica-related-physiological-effects",totalDownloads:40,totalDimensionsCites:0,doi:"10.5772/intechopen.102450",abstract:"Phytoremediation is a technique for treatment areas with medium or low heavy metals concentrations. A pot experiment was carried out to determine the usefulness of Canna indica L. as phytoremediator species. The plants were treated with three increasing Zn(II) and Cu(II) solutions. 21 days later, dry weight, relative membrane conductivity, chlorophyll, carotene, malondialdehyde, soluble proteins, proline, and Zn(II) and Cu(II) contents were measured. Zn(II) and Cu (II) treatments caused a decline in the dry weight, chlorophyll, carotene, and soluble proteins content, whereas the relative conductivity, malondialdehyde, and proline content showed the opposite pattern. The bioaccumulation reached values approximately 48 and 15 times higher (5293 mg kg−1 and 1425 mg kg−1), compared with the control, for Zn(II) and Cu(II), respectively. Our results suggest that this species can be used for the phytoremediation of polluted soils with moderate concentrations of Zn(II) and Cu(II).",book:{id:"11120",title:"Environmental Impact and Remediation of Heavy Metals",coverURL:"https://cdn.intechopen.com/books/images_new/11120.jpg"},signatures:"Josefina Plaza Cazón, Matías Gonzalez and Marcela Ruscitti"},{id:"80534",title:"Toxicants in Water: Hydrochemical Appraisal of Toxic Metals Concentration and Seasonal Variation in Drinking Water Quality in Oil and Gas Field Area of Rivers State, Nigeria",slug:"toxicants-in-water-hydrochemical-appraisal-of-toxic-metals-concentration-and-seasonal-variation-in-d",totalDownloads:52,totalDimensionsCites:1,doi:"10.5772/intechopen.102656",abstract:"Groundwater pollution is a major issue in many tropical countries. Governments at all levels are doing little or nothing to supply inhabitants with clean and accessible water, particularly in Nigeria’s Niger Delta region. This study compares differences in water quality parameters in the study area (determine the level of pollutions in the different sites). The investigation made use of standard analytical methodologies. All sampling, conservation, transportation as well as analysis followed the usual APHA procedures (2012). To prevent degradation of the organic substances, all obtained samples were transferred to the laboratory, while keeping in an icebox. Result shows that during wet season, the mean values obtained for water quality parameters were significantly lower in site 9 compared with that obtained in other sites (p < 0.05) with the exemptions of temperature, DO, BOD, COD, acidity, TH, TDS, K, Mg, Zn, Mn, Cd, Pb, Cu, Cr, NH3, NO2, NO3, Ni though slightly lower in most cases in site 9 were not significantly different (p > 0.05) and both alkalinity and SO4 which were significantly higher in site 9 than site 1 (p < 0.05). Result obtained during dry season reveals that there is no remarkable difference in pH, acidity, Pb and Ni between the nine sites (p > 0.05) while other water quality parameters were significantly lower in site 9 than other sites excluding Cl and Mg which were both significantly higher in site 9 than site 8 (p < 0.05). Extra efforts must be made to completely understand the hydrogeochemical properties and appropriateness of groundwater in Nigeria’s core Niger Delta region in order to ensure quality groundwater supply for varied applications. As a result, this research will contribute to the establishment of a quantitative understanding of the effects of many causes on groundwater level changes in every aquifer worldwide. This analysis also reinforces a useful resource for scholars, activists, and public officials looking to improve community awareness, planning, and performance. The verdicts will serve as a valuable guideline for policymakers, the Ministry of Water Resources, and development practitioners, as they highlight the need for appropriate approaches to mitigating toxic elements of water resource contamination in the core Niger Delta in order to protect public health from carcinogenic and non-carcinogenic risks.",book:{id:"11120",title:"Environmental Impact and Remediation of Heavy Metals",coverURL:"https://cdn.intechopen.com/books/images_new/11120.jpg"},signatures:"Morufu Olalekan Raimi, Henry Olawale Sawyerr, Ifeanyichukwu Clinton Ezekwe and Salako Gabriel"}],onlineFirstChaptersTotal:12},preDownload:{success:null,errors:{}},subscriptionForm:{success:null,errors:{}},aboutIntechopen:{},privacyPolicy:{},peerReviewing:{},howOpenAccessPublishingWithIntechopenWorks:{},sponsorshipBooks:{sponsorshipBooks:[],offset:0,limit:8,total:null},allSeries:{pteSeriesList:[{id:"14",title:"Artificial Intelligence",numberOfPublishedBooks:9,numberOfPublishedChapters:87,numberOfOpenTopics:6,numberOfUpcomingTopics:0,issn:"2633-1403",doi:"10.5772/intechopen.79920",isOpenForSubmission:!0},{id:"7",title:"Biomedical Engineering",numberOfPublishedBooks:12,numberOfPublishedChapters:99,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2631-5343",doi:"10.5772/intechopen.71985",isOpenForSubmission:!0}],lsSeriesList:[{id:"11",title:"Biochemistry",numberOfPublishedBooks:27,numberOfPublishedChapters:289,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2632-0983",doi:"10.5772/intechopen.72877",isOpenForSubmission:!0},{id:"25",title:"Environmental Sciences",numberOfPublishedBooks:1,numberOfPublishedChapters:9,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2754-6713",doi:"10.5772/intechopen.100362",isOpenForSubmission:!0},{id:"10",title:"Physiology",numberOfPublishedBooks:11,numberOfPublishedChapters:139,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2631-8261",doi:"10.5772/intechopen.72796",isOpenForSubmission:!0}],hsSeriesList:[{id:"3",title:"Dentistry",numberOfPublishedBooks:8,numberOfPublishedChapters:129,numberOfOpenTopics:0,numberOfUpcomingTopics:2,issn:"2631-6218",doi:"10.5772/intechopen.71199",isOpenForSubmission:!1},{id:"6",title:"Infectious Diseases",numberOfPublishedBooks:13,numberOfPublishedChapters:108,numberOfOpenTopics:3,numberOfUpcomingTopics:1,issn:"2631-6188",doi:"10.5772/intechopen.71852",isOpenForSubmission:!0},{id:"13",title:"Veterinary Medicine and Science",numberOfPublishedBooks:11,numberOfPublishedChapters:104,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2632-0517",doi:"10.5772/intechopen.73681",isOpenForSubmission:!0}],sshSeriesList:[{id:"22",title:"Business, Management and Economics",numberOfPublishedBooks:1,numberOfPublishedChapters:12,numberOfOpenTopics:2,numberOfUpcomingTopics:1,issn:"2753-894X",doi:"10.5772/intechopen.100359",isOpenForSubmission:!0},{id:"23",title:"Education and Human Development",numberOfPublishedBooks:0,numberOfPublishedChapters:0,numberOfOpenTopics:2,numberOfUpcomingTopics:0,issn:null,doi:"10.5772/intechopen.100360",isOpenForSubmission:!1},{id:"24",title:"Sustainable Development",numberOfPublishedBooks:0,numberOfPublishedChapters:11,numberOfOpenTopics:4,numberOfUpcomingTopics:1,issn:null,doi:"10.5772/intechopen.100361",isOpenForSubmission:!0}],testimonialsList:[{id:"6",text:"It is great to work with the IntechOpen to produce a worthwhile collection of research that also becomes a great educational resource and guide for future research endeavors.",author:{id:"259298",name:"Edward",surname:"Narayan",institutionString:null,profilePictureURL:"https://mts.intechopen.com/storage/users/259298/images/system/259298.jpeg",slug:"edward-narayan",institution:{id:"3",name:"University of Queensland",country:{id:null,name:"Australia"}}}},{id:"13",text:"The collaboration with and support of the technical staff of IntechOpen is fantastic. The whole process of submitting an article and editing of the submitted article goes extremely smooth and fast, the number of reads and downloads of chapters is high, and the contributions are also frequently cited.",author:{id:"55578",name:"Antonio",surname:"Jurado-Navas",institutionString:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRisIQAS/Profile_Picture_1626166543950",slug:"antonio-jurado-navas",institution:{id:"720",name:"University of Malaga",country:{id:null,name:"Spain"}}}}]},series:{item:{id:"7",title:"Biomedical Engineering",doi:"10.5772/intechopen.71985",issn:"2631-5343",scope:"Biomedical Engineering is one of the fastest-growing interdisciplinary branches of science and industry. The combination of electronics and computer science with biology and medicine has improved patient diagnosis, reduced rehabilitation time, and helped to facilitate a better quality of life. Nowadays, all medical imaging devices, medical instruments, or new laboratory techniques result from the cooperation of specialists in various fields. The series of Biomedical Engineering books covers such areas of knowledge as chemistry, physics, electronics, medicine, and biology. 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Dr. Koprowski has authored more than a hundred research papers with dozens in impact factor (IF) journals and has authored or co-authored six books. Additionally, he is the author of several national and international patents in the field of biomedical devices and imaging. 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