Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health

Heavy metal pollution is a major public health concern. Mercury (Hg) and Lead (Pb) are widespread heavy metals, recognized as global contaminants. These harmful chemicals are normally present in nature, but different anthropogenic activities have increased biota and human exposure. Among these activ...

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Autores:
Carranza López, Liliana Patricia
Tipo de recurso:
Doctoral thesis
Fecha de publicación:
2020
Institución:
Universidad de Cartagena
Repositorio:
Repositorio Universidad de Cartagena
Idioma:
eng
OAI Identifier:
oai:repositorio.unicartagena.edu.co:11227/18831
Acceso en línea:
https://hdl.handle.net/11227/18831
Palabra clave:
Mercury
Liquid metals
Liquid iron
Environmental monitoring
Rights
openAccess
License
https://creativecommons.org/licenses/by-nc/4.0/
id UCART2_89c713bf7843dba3f5499f0b5c888354
oai_identifier_str oai:repositorio.unicartagena.edu.co:11227/18831
network_acronym_str UCART2
network_name_str Repositorio Universidad de Cartagena
repository_id_str
dc.title.eng.fl_str_mv Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
title Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
spellingShingle Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
Mercury
Liquid metals
Liquid iron
Environmental monitoring
title_short Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
title_full Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
title_fullStr Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
title_full_unstemmed Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
title_sort Biomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human health
dc.creator.fl_str_mv Carranza López, Liliana Patricia
dc.contributor.advisor.none.fl_str_mv Olivero Verbel, Jesús
dc.contributor.author.none.fl_str_mv Carranza López, Liliana Patricia
dc.subject.armarc.none.fl_str_mv Mercury
Liquid metals
Liquid iron
Environmental monitoring
topic Mercury
Liquid metals
Liquid iron
Environmental monitoring
description Heavy metal pollution is a major public health concern. Mercury (Hg) and Lead (Pb) are widespread heavy metals, recognized as global contaminants. These harmful chemicals are normally present in nature, but different anthropogenic activities have increased biota and human exposure. Among these activities, Hg is used in gold mining and Pb in fishing tools manufacture. This is critical at developing countries, where those represent a significant environmental risk for the population, especially for vulnerable communities. In Colombia, Hg is highly used in gold mining activities, most carried out as the only economic activity for many families. The lack of good practices and technological tools allows Hg to reach nearby ecosystems, where it can be bioaccumulated in the food web and human. Therefore, high Hg concentrations have been found in carnivorous fish and humans. In this sense, this study was carried out to evaluate total Hg (T-Hg) concentrations in human hair, fish, soil, and air from two major gold-mining districts (GMDs), the Mojana region and the Middle Magdalena in the department of Bolivar, Colombia. Total Hg (T-Hg) concentrations were evaluated at two major GMDs, at the department of Bolivar. Total Hg was analyzed using a direct Hg analyzer. Average T-Hg level in hair samples was 3.07 ± 0.14 μg/g (range 0.15–25.1 μg/g; median 2.02 μg/g). The highest Hg level was observed in Mojana GMD, specifically at Achi-La Raya (9.2 ± 0.6 μg/g) and the lowest in Morales, at the Middle Magdalena GMD (1.50 ± 0.16 μg/g). Hair T-Hg values exceeded the U.S. Environmental Protection Agency (USEPA) reference level of 1.0 μg/g. Total Hg fish concentrations were evaluated in several fish species, including, Caquetaia kraussii, Sorubim cuspicaudus, 8 Plagioscion surinamensis, Trachelyopterus insignis, Prochilodus magdalenae and Pseudoplatystoma magdaleniatum. The highest average T-Hg fish concentration was observed in Caquetaia kraussii (0.37 ± 0.10 μg/g), whereas the lowest (0.03 ± 0.01 μg/g) was reported in Prochilodus magdalenae. Human health risk assessment of Hg exposure, based on fish consumption, suggested that, with the exception of P. magdalenae, all economically significant fish species are potentially harmful for the communities. Soil Hg levels in amalgam burning facilities were extremely high, and Hg in the air around mining areas and gold-processing shops exceeded international guidelines. Mercury is not the only chemical threat in vulnerable populations. Currently, Pb is particularly influential as a pollutant in many fishing communities. Children are highly vulnerable to Pb poisoning because this metal has the potential to exert deleterious effects, in particular at the nervous system, causing cognitive deficits, behavioral problems, on the other hand, anemia, infertility, hepatic effects, hearing impairment, immune-related diseases, decreased physical growth, and hypertension, among others. Thus, in this study Blood lead levels (BLL) were assessed in children from two fishing communities in Northern Colombia, Loma de Arena and Tierrabomba, evaluating their association with morphometric parameters, markers of hematological status, liver function, and mRNA expression of genes related to Pb toxicity. A total of 198 blood samples were collected from participants aged 5–16 years old. The mean (± standard error) BLL for the studied sample was 3.6 ± 0.3 μg/dL. The participants of Loma de Arena and Tierrabomba presented BLL of 3.9 ± 0.5 and 2.9 ± 0.3 μg/dL, respectively. 9 Children born preterm had greater BLL than those born at full term. Boys had greater BLL than girls, which also occurred for participants between 12 and 16 years old, compared with those aged 5–11 years old. The BLL were negatively correlated with body mass index in children from Loma de Arena, but an opposite behavior was observed for Tierrabomba. In Loma de Arena, the mRNA expression of interferon gamma, a pro-inflammatory cytokine, increased with the BLL, while that of δ-aminolevulinic acid dehydrogenase, a sensor for Pb poisoning, decreased. In Tierrabomba, gene expression did not change with BLL. In conclusion, these results show that in fishing communities lead exposure promotes different health impacts depending on age, sex, and other site-specific factors. In any case, appropriate educational and intervention programs should be carried out to minimize Pb exposure in children.
publishDate 2020
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dc.relation.references.none.fl_str_mv Abbondanzi, F., Cachada, A., Campisi, T., Guerra, R., Raccagni, M., Iacondini, A. 2003. Optimisation of a microbial bioassay for contaminated soil monitoring: bacterial inoculum standardisation and comparison with Microtox® assay. Chemosphere. 53(8):889-897.
Akagi, H., Ikingura, J.R. 1996. Monitoring of fish and human exposure to mercury due to gold mining in the Lake Victoria goldfields, Tanzania. Sci. Total Environ. 191:59- 68.
Akram, Z., Riaz, S., Kayani, M.A., Jahan, S., Ahmad, M.W., Ullah, M.A., Wazir, H., Mahjabeen, I. 2019. Lead induces DNA damage and alteration of ALAD and antioxidant genes mRNA expression in construction site workers. Arch. Environ. Occup. Health 74(4):171-178.
Alabi, O.A., Bakare, A.A., Xu, X., Li, B., Zhang, Y., Huo, X. 2012. Comparative evaluation of environmental contamination and DNA damage induced by electronic-waste in Nigera and China. Sci. Total Environ. 423:62-72.
Alcala-Orozco, M., Caballero-Gallardo, K., & Olivero-Verbel, J. (2019). Mercury exposure assessment in indigenous communities from Tarapaca village, Cotuhe and Putumayo Rivers, Colombian Amazon. Environmental science and pollution research international, 26(36), 36458–36467.
Alvarez-Ortega, N., Caballero-Gallardo, K., Olivero-Verbel, J. 2019. Toxicological effects in children exposed to lead: a crosssectional study at the Colombian Caribbean coast. Environ. Int. 130:104809.
Alvarez-Ortega, N., Caballero-Gallardo, K., Olivero-Verbel, J. 2017. AlexisLow blood lead levels impair intellectual and hematological function in children from Cartagena, Caribbean coast of Colombia. J. Trace Elem. Med. Biol. 44:233-240.
Anticona, C., Bergdahl, I.A., San Sebastian, M. 2012. Lead exposure among children from native communities of the Peruvian Amazon basin. Rev Panam Salud Publica 31:296-302.
Ashe, K. 2012. Elevated mercury concentrations in humans of Madre de Dios, Peru. PLoS ONE 7:e33305.
ATSDR. 2007. Agency for Toxic Substances and Disease Registry. Health Consultation. https ://www.atsdr .cdc.gov/HAC/pha/Kings fordM iddle Schoo l/Kings fordM iddle Schoo lHC03 3007.pdf.
ATSDR, 2007. Toxicological profile for lead. Atlanta, GA: US Department of Health and Human Services, Public Health Service. Agency for Toxic Substances and Disease Registry. Division of Toxicology and Environmental Medicine/Applied Toxicology Branch; http://www.atsdr. cdc.gov/toxprofiles/tp13.pdf.
ASTDR. 1999. Agency for Toxic Substances and Disease Registry. Department of Health and Human Services. Public Health Service; Atlanta, GA, USA: 1999. Toxicological profile for mercury
ATSDR. 2005. Agency for Toxic Substances and Disease Registry (ATSDR). Toxicological profile for lead. Atlanta, GA: US Department of Health and Human Services. 102–225.
Axelrad, D.A., Bellinger, D.C., Ryan, L.M., Woodruff, T.J. 2007. Doseresponse relationship of prenatal mercury exposure and IQ: an integrative analysis of epidemiologic data. Environ. Health Perspect. 115: 609-615.
Basu, N., Horvat, M., Evers, D. C., Zastenskaya, I., Weihe, P., & Tempowski, J. 2018. A State-of-the-Science Review of Mercury Biomarkers in Human Populations Worldwide between 2000 and 2018. Environ. Health Perspectives. 126(10):106001.
Berrow, M., Reaves, G. 1984. Background of trace elements in soils. In: Proceedings 1st international conference on environmental contamination. CEP Consultants, Edinburg, pp 333-340.
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spelling Olivero Verbel, JesúsCarranza López, Liliana Patricia2025-02-17T15:43:05Z2025-02-17T15:43:05Z2020https://hdl.handle.net/11227/18831Heavy metal pollution is a major public health concern. Mercury (Hg) and Lead (Pb) are widespread heavy metals, recognized as global contaminants. These harmful chemicals are normally present in nature, but different anthropogenic activities have increased biota and human exposure. Among these activities, Hg is used in gold mining and Pb in fishing tools manufacture. This is critical at developing countries, where those represent a significant environmental risk for the population, especially for vulnerable communities. In Colombia, Hg is highly used in gold mining activities, most carried out as the only economic activity for many families. The lack of good practices and technological tools allows Hg to reach nearby ecosystems, where it can be bioaccumulated in the food web and human. Therefore, high Hg concentrations have been found in carnivorous fish and humans. In this sense, this study was carried out to evaluate total Hg (T-Hg) concentrations in human hair, fish, soil, and air from two major gold-mining districts (GMDs), the Mojana region and the Middle Magdalena in the department of Bolivar, Colombia. Total Hg (T-Hg) concentrations were evaluated at two major GMDs, at the department of Bolivar. Total Hg was analyzed using a direct Hg analyzer. Average T-Hg level in hair samples was 3.07 ± 0.14 μg/g (range 0.15–25.1 μg/g; median 2.02 μg/g). The highest Hg level was observed in Mojana GMD, specifically at Achi-La Raya (9.2 ± 0.6 μg/g) and the lowest in Morales, at the Middle Magdalena GMD (1.50 ± 0.16 μg/g). Hair T-Hg values exceeded the U.S. Environmental Protection Agency (USEPA) reference level of 1.0 μg/g. Total Hg fish concentrations were evaluated in several fish species, including, Caquetaia kraussii, Sorubim cuspicaudus, 8 Plagioscion surinamensis, Trachelyopterus insignis, Prochilodus magdalenae and Pseudoplatystoma magdaleniatum. The highest average T-Hg fish concentration was observed in Caquetaia kraussii (0.37 ± 0.10 μg/g), whereas the lowest (0.03 ± 0.01 μg/g) was reported in Prochilodus magdalenae. Human health risk assessment of Hg exposure, based on fish consumption, suggested that, with the exception of P. magdalenae, all economically significant fish species are potentially harmful for the communities. Soil Hg levels in amalgam burning facilities were extremely high, and Hg in the air around mining areas and gold-processing shops exceeded international guidelines. Mercury is not the only chemical threat in vulnerable populations. Currently, Pb is particularly influential as a pollutant in many fishing communities. Children are highly vulnerable to Pb poisoning because this metal has the potential to exert deleterious effects, in particular at the nervous system, causing cognitive deficits, behavioral problems, on the other hand, anemia, infertility, hepatic effects, hearing impairment, immune-related diseases, decreased physical growth, and hypertension, among others. Thus, in this study Blood lead levels (BLL) were assessed in children from two fishing communities in Northern Colombia, Loma de Arena and Tierrabomba, evaluating their association with morphometric parameters, markers of hematological status, liver function, and mRNA expression of genes related to Pb toxicity. A total of 198 blood samples were collected from participants aged 5–16 years old. The mean (± standard error) BLL for the studied sample was 3.6 ± 0.3 μg/dL. The participants of Loma de Arena and Tierrabomba presented BLL of 3.9 ± 0.5 and 2.9 ± 0.3 μg/dL, respectively. 9 Children born preterm had greater BLL than those born at full term. Boys had greater BLL than girls, which also occurred for participants between 12 and 16 years old, compared with those aged 5–11 years old. The BLL were negatively correlated with body mass index in children from Loma de Arena, but an opposite behavior was observed for Tierrabomba. In Loma de Arena, the mRNA expression of interferon gamma, a pro-inflammatory cytokine, increased with the BLL, while that of δ-aminolevulinic acid dehydrogenase, a sensor for Pb poisoning, decreased. In Tierrabomba, gene expression did not change with BLL. In conclusion, these results show that in fishing communities lead exposure promotes different health impacts depending on age, sex, and other site-specific factors. In any case, appropriate educational and intervention programs should be carried out to minimize Pb exposure in children.DoctoradoDoctor(a) en Toxicología Ambientalapplication/pdfengUniversidad de CartagenaFacultad de Ciencias FarmacéuticasCartagena de IndiasDoctorado en Toxicología Ambientalhttps://creativecommons.org/licenses/by-nc/4.0/Atribución-NoComercial 4.0 Internacional (CC BY-NC 4.0)http://purl.org/coar/access_right/c_abf2info:eu-repo/semantics/openAccessBiomonitoring of mercury and lead in vulnerable communities of the Colombian Caribbean: Exposure and impacts on human healthTrabajo de grado - Doctoradoinfo:eu-repo/semantics/publishedVersionhttp://purl.org/coar/version/c_970fb48d4fbd8a85http://purl.org/coar/resource_type/c_db06Textinfo:eu-repo/semantics/doctoralThesisAbbondanzi, F., Cachada, A., Campisi, T., Guerra, R., Raccagni, M., Iacondini, A. 2003. Optimisation of a microbial bioassay for contaminated soil monitoring: bacterial inoculum standardisation and comparison with Microtox® assay. Chemosphere. 53(8):889-897.Akagi, H., Ikingura, J.R. 1996. Monitoring of fish and human exposure to mercury due to gold mining in the Lake Victoria goldfields, Tanzania. Sci. Total Environ. 191:59- 68.Akram, Z., Riaz, S., Kayani, M.A., Jahan, S., Ahmad, M.W., Ullah, M.A., Wazir, H., Mahjabeen, I. 2019. Lead induces DNA damage and alteration of ALAD and antioxidant genes mRNA expression in construction site workers. Arch. Environ. Occup. Health 74(4):171-178.Alabi, O.A., Bakare, A.A., Xu, X., Li, B., Zhang, Y., Huo, X. 2012. Comparative evaluation of environmental contamination and DNA damage induced by electronic-waste in Nigera and China. Sci. Total Environ. 423:62-72.Alcala-Orozco, M., Caballero-Gallardo, K., & Olivero-Verbel, J. (2019). Mercury exposure assessment in indigenous communities from Tarapaca village, Cotuhe and Putumayo Rivers, Colombian Amazon. Environmental science and pollution research international, 26(36), 36458–36467.Alvarez-Ortega, N., Caballero-Gallardo, K., Olivero-Verbel, J. 2019. Toxicological effects in children exposed to lead: a crosssectional study at the Colombian Caribbean coast. Environ. Int. 130:104809.Alvarez-Ortega, N., Caballero-Gallardo, K., Olivero-Verbel, J. 2017. AlexisLow blood lead levels impair intellectual and hematological function in children from Cartagena, Caribbean coast of Colombia. J. Trace Elem. Med. Biol. 44:233-240.Anticona, C., Bergdahl, I.A., San Sebastian, M. 2012. Lead exposure among children from native communities of the Peruvian Amazon basin. Rev Panam Salud Publica 31:296-302.Ashe, K. 2012. Elevated mercury concentrations in humans of Madre de Dios, Peru. PLoS ONE 7:e33305.ATSDR. 2007. Agency for Toxic Substances and Disease Registry. Health Consultation. https ://www.atsdr .cdc.gov/HAC/pha/Kings fordM iddle Schoo l/Kings fordM iddle Schoo lHC03 3007.pdf.ATSDR, 2007. Toxicological profile for lead. Atlanta, GA: US Department of Health and Human Services, Public Health Service. Agency for Toxic Substances and Disease Registry. Division of Toxicology and Environmental Medicine/Applied Toxicology Branch; http://www.atsdr. cdc.gov/toxprofiles/tp13.pdf.ASTDR. 1999. Agency for Toxic Substances and Disease Registry. Department of Health and Human Services. Public Health Service; Atlanta, GA, USA: 1999. Toxicological profile for mercuryATSDR. 2005. Agency for Toxic Substances and Disease Registry (ATSDR). Toxicological profile for lead. Atlanta, GA: US Department of Health and Human Services. 102–225.Axelrad, D.A., Bellinger, D.C., Ryan, L.M., Woodruff, T.J. 2007. Doseresponse relationship of prenatal mercury exposure and IQ: an integrative analysis of epidemiologic data. Environ. Health Perspect. 115: 609-615.Basu, N., Horvat, M., Evers, D. C., Zastenskaya, I., Weihe, P., & Tempowski, J. 2018. A State-of-the-Science Review of Mercury Biomarkers in Human Populations Worldwide between 2000 and 2018. Environ. Health Perspectives. 126(10):106001.Berrow, M., Reaves, G. 1984. Background of trace elements in soils. In: Proceedings 1st international conference on environmental contamination. CEP Consultants, Edinburg, pp 333-340.MercuryLiquid metalsLiquid ironEnvironmental monitoringPublicationORIGINAL2020_TESIS DE GRADO_LILIANA CARRANZA LOPEZ.pdf2020_TESIS DE GRADO_LILIANA CARRANZA LOPEZ.pdfapplication/pdf3269988https://repositorio.unicartagena.edu.co/bitstreams/39b87e93-9606-4d2b-b4dd-ba6e822a7694/downloadf558e520a55c070d9a2f294edc9aacafMD51FORMATO CESION DE DERECHOS DE AUTOR_GRADO_LILIANA CARRANZA.pdfFORMATO CESION DE DERECHOS DE AUTOR_GRADO_LILIANA CARRANZA.pdfapplication/pdf221281https://repositorio.unicartagena.edu.co/bitstreams/de8461f1-2b4c-4d1c-ba95-de5315779091/download472b0c93d5f111f11f35788c51f347f4MD52LICENSElicense.txtlicense.txttext/plain; charset=utf-81802https://repositorio.unicartagena.edu.co/bitstreams/0b23a374-cd1e-48a2-b30e-e09978e2eeb8/download64eb6cdbc122cfe492fa78c8434a0f6bMD53TEXT2020_TESIS DE GRADO_LILIANA CARRANZA LOPEZ.pdf.txt2020_TESIS DE GRADO_LILIANA CARRANZA LOPEZ.pdf.txtExtracted texttext/plain101297https://repositorio.unicartagena.edu.co/bitstreams/207157a0-ff33-4ffb-9dbe-f9ae2a3c1b76/download66c523cdd83da094af6634422d7cd7abMD54FORMATO CESION DE DERECHOS DE AUTOR_GRADO_LILIANA CARRANZA.pdf.txtFORMATO CESION DE DERECHOS DE AUTOR_GRADO_LILIANA CARRANZA.pdf.txtExtracted texttext/plain2936https://repositorio.unicartagena.edu.co/bitstreams/707c3de2-f0d6-4a46-b875-6cbd4d8e6bbf/download05350ab126c9ba062632797c215c02e3MD56THUMBNAIL2020_TESIS DE GRADO_LILIANA CARRANZA LOPEZ.pdf.jpg2020_TESIS DE GRADO_LILIANA CARRANZA LOPEZ.pdf.jpgGenerated Thumbnailimage/jpeg7431https://repositorio.unicartagena.edu.co/bitstreams/701ca775-4fb7-4a70-95af-60ca2823e7e8/download6d5252cf734ac84c03de02559b43aed8MD55FORMATO CESION DE DERECHOS DE AUTOR_GRADO_LILIANA CARRANZA.pdf.jpgFORMATO CESION DE DERECHOS DE AUTOR_GRADO_LILIANA CARRANZA.pdf.jpgGenerated Thumbnailimage/jpeg15943https://repositorio.unicartagena.edu.co/bitstreams/765eaf06-e41d-4e8d-b8e4-94902b6eb880/download82a4e16bebb549acaaa938f37bd4b96eMD5711227/18831oai:repositorio.unicartagena.edu.co:11227/188312025-02-18 05:01:01.863https://creativecommons.org/licenses/by-nc/4.0/open.accesshttps://repositorio.unicartagena.edu.coBiblioteca Digital Universidad de Cartagenabdigital@metabiblioteca.comPHA+QWwgZmlybWFyIHkgcHJlc2VudGFyIGVzdGEgbGljZW5jaWEsIHVzdGVkIChBVVRPUiBPIEFVVE9SRVMpICBvIGxvcyBkZXJlY2hvcyBkZSBhdXRvciBkZWwgcHJvcGlldGFyaW8oUykgZ2FyYW50aXphIGEgIGxhIFVOSVZFUlNJREFEIERFIENBUlRBR0VOQSBlbCBkZXJlY2hvIGV4Y2x1c2l2byBkZSByZXByb2R1Y2lyLCB0cmFkdWNpciAoY29tbyBzZSBkZWZpbmUgbcOhcyBhZGVsYW50ZSkgeS9vIGRpc3RyaWJ1aXIgc3UgZG9jdW1lbnRvIChpbmNsdXllbmRvIGVsIHJlc3VtZW4pIGVuIHRvZG8gZWwgbXVuZG8gIGVuIGZvcm1hIGltcHJlc2EgeSBlbiBmb3JtYXRvIGVsZWN0csOzbmljbyB5IGVuIGN1YWxxdWllciBtZWRpbywgaW5jbHV5ZW5kbyBhdWRpbyBvIHZpZGVvLjwvcD4KCjxwPlVzdGVkIGFjZXB0YSBxdWUgbGEgVU5JVkVSU0lEQUQgREUgQ0FSVEFHRU5BICBwdWVkZSwgc2luIGNhbWJpYXIgZWwgY29udGVuaWRvIGNvbnZlcnRpcmxvLCBwcmVzZW50YXJsbyAgYSBjdWFscXVpZXIgbWVkaW8gbyBmb3JtYXRvIHBhcmEgbG9zIGZpbmVzIGRlIGNvbnNlcnZhY2nDs24uPC9wPgoKPHA+VXN0ZWQgdGFtYmnDqW4gYWNlcHRhIHF1ZSBsYSBVTklWRVJTSURBRCBERSBDQVJUQUdFTkEgICBwdWVkYSBjb25zZXJ2YXIgbcOhcyBkZSB1bmEgY29waWEgZGUgZXN0ZSBkb2N1bWVudG8gcGFyYSBmaW5lcyBkZSBzZWd1cmlkYWQgeSBwcmVzZXJ2YWNpw7NuLjwvcD4KCjxwPlVzdGVkIGRlY2xhcmEgcXVlIGVsIGRvY3VtZW50byBlcyB1biB0cmFiYWpvIG9yaWdpbmFsIHkgIHF1ZSB0aWVuZSBlbCBkZXJlY2hvIGRlIG90b3JnYXIgbG9zIGRlcmVjaG9zIGNvbnRlbmlkb3MgZW4gZXN0YSBsaWNlbmNpYS4gIFRhbWJpw6luIHJlcHJlc2VudGFuICBsbyBtZWpvciBkZSBzdSBjb25vY2ltaWVudG8geSBubyBpbmZyaW5nZW4gIGxvcyBkZXJlY2hvcyBkZSBhdXRvciBkZSBuYWRpZS48L3A+Cgo8cD5TaSBlbCBkb2N1bWVudG8gY29udGllbmUgbWF0ZXJpYWxlcyBkZSBsb3MgcXVlIG5vIHRpZW5lIGxvcyAgZGVyZWNob3MgZGUgYXV0b3IsIHVzdGVkIGRlY2xhcmEgcXVlIGhhIG9idGVuaWRvIGVsIHBlcm1pc28gc2luIHJlc3RyaWNjacOzbiBkZWwgcHJvcGlldGFyaW8gZGUgbG9zIGRlcmVjaG9zLCBkYSBhIGNvbmNlZGVyICBsb3MgZGVyZWNob3MgcmVxdWVyaWRvcyBwb3IgZXN0YSBsaWNlbmNpYSwgeSBxdWUgY29tbyBtYXRlcmlhbCBwcm9waWVkYWQgIGRlIHRlcmNlcm9zICBlc3TDoSBjbGFyYW1lbnRlIGlkZW50aWZpY2FkbyB5IHJlY29ub2NpZG8gZGVudHJvIGRlbCB0ZXh0byBvIGVsIGNvbnRlbmlkbyBkZSBsYSBwcmVzZW50YWNpw7NuLjwvcD4KCjxwPlNpIGxhIHByZXNlbnRhY2nDs24gc2UgYmFzYSBlbiAgdHJhYmFqb3MgUVVFIFNFIEhBIHBhdHJvY2luYWRvIG8gYXBveWFkbyBQT1IgVU5BIEFHRU5DSUEgVSBPUkdBTklaQUNJw5NOIFFVRSBOTyBTRUEgTEEgVU5JVkVSU0lEQUQgREUgQ0FSVEFHRU5BLCBNQU5JRklFU1RBIFFVRSBUSUVORSBRVUUgQ1VNUExJUiBkZXJlY2hvcyBhIHJldmlzacOzbiB1IG90cmFzIG9ibGlnYWNpb25lcyBxdWUgZXhpZ2VuIGVzdGUgQ29udHJhdG8gbyBhY3VlcmRvLjwvcD4KCjxwPkRpY2UgcXVlIGlkZW50aWZpY2Fyw6EgY2xhcmFtZW50ZSBzdSBub21icmUgKHMpIGNvbW8gZWwgYXV0b3IgKHMpIG8gcHJvcGlldGFyaW8gKGEpIGRlIGxvcyBkb2N1bWVudG8geSBubyBoYXLDoSBuaW5ndW5hIGFsdGVyYWNpw7NuLCBleGVudG8gbGFzIHBlcm1pdGlkYXMgZW4gZXN0YSBsaWNlbmNpYSBwYXJhIHN1IHByZXNlbnRhY2nDs24uPC9wPgo=