• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2002년도 총회 및 춘계학술발표회
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• pp.347-350
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• 2002

Arsenic speciation changes between As(V) and As(III) are subject to changes in accordance with redox conditions in the environment. It is common to find contaminated sites associated with mixed wastes including both organic pollutants and heavy metals. We conducted microcosm experiment under hypothesis that the co-disposed organic pollutants would influence on the arsenic forms and concentrations, via degradation of the organic pollutants and the consequent impact on the redox conditions in soil. Artificially contaminated soil samples were run for 40 days with control samples without artificial contamination. We noticed arsenic in the contaminated soil showed different behaviour compared with the arsenic in the control soil. The findings indicate degradation of organic pollutants in the contaminated soil influenced on the arsenic speciation and concentrations. A further work is needed to understand the process quantitatively. However, we could confirm that degradation of organic pollutants can influence on the abiotic processes associated with geochemical reactions in contaminated soil. Degradation of organic pollutants can increase the mobility and toxicity of arsenic in soil and sediment by changing redox conditions in the geological media and subsequently from As(V) to As(III).

• Journal of Applied Biological Chemistry
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• 제51권1호
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• pp.36-44
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• 2008

Organic forms of arsenic (As) were determined through fractionation procedure of soil organic matter (SOM) in soil, sediments and mine tailing samples from the Myungbong, Dongil, and Okdong mining areas of southern Korea. An alkaline extraction method was applied to soil samples followed by the fractionation procedures of SOM by the DAX-8 and XAD-4 resin adsorption method. Major fraction of organic As species (42% to 98%) was found in acid-soluble fraction, whereas minor fraction (0.1 % to 67.8%) was present in the humic-associated As. In acid-soluble fractions, the transphillic- and hydrophilic-associated As were dominant in addition to As binding with humic and fulvic SOM. Arsenic binding was the strongest between pH 6 to 8 and reduced to about 70% at both low and high pH regions. The amount of both transphillic and hydrophillic associated As was less changed than humic and fulvic-associated As, in both low and high pH regions. This apparently indicates that As has stronger affinity towards hydrophillic rather than hydrophobic organics. From the experimental observation of As-binding SOM in natural soil, the ligand exchange model may be a feasible explanation of transphillic and hydrophillic affinity of As.

• Toxicological Research
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• 제24권3호
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• pp.219-225
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• 2008

A screening study of the acute toxicity of organic arsenics such as arsenobetaine and arsenocholine, a product of arsenic methylation metabolite, and inorganic arsenic was carried out to examine hematological and serum biochemical parameters in cynomolgus monkeys(Macaca fascicularis). We found soft and liquid feces, and vomiting in all treated groups with inorganic and organic arsenics. The monkeys in inorganic arsenic-treated group showed a significant increase in vomiting frequency compared with those in three organic arsenics-treated groups. These results suggest that inorganic arsenic might be more toxic than three other organic arsenics tested. The monkeys in inorganic arsenic-treated group showed a decrease in platelet and an increase in monocyte on day 4 and the monkeys in arsenocholine-treated group showed an increase in reticulocyte percentage on day 8. The monkeys in inorganic-treated group also showed decreases in AST and ALT values and the monkeys in arsenobetaine-treated group showed a decrease in AST value and an increase in T-CHO value. However, these hematological and biochemical changes were within the physiological ranges, showing that the single dose of inorganic and organic arsenics did not affect at least hematological and serum biochemical parameters. The present study of toxicity with single dose of arsenics provides valuable indicators for longer term study of toxicity of repeated doses of arsenics in primates.

• Toxicological Research
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• 제18권2호
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• pp.107-116
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• 2002

Arsenic (As) is a ubiquitous element found in several forms in foods and water. Although certain foods, such as marine fish, contain substantial levels of organic arsenic forms, they are relatively low in toxicity compared to inorganic forms. in contrast, arsenic in drinking water is predominantly inorganic and highly toxic. Chronic ingestion of arsenic-contaminated drinking water is therefore the major pathway posing potential risk to human hearth. since the early 1990s in Bangladesh ozone, arsenic exposure has caused more than 7,000 deaths and uncounted thousands shout symptoms of long-term arsenic poisoning. Significant portion of world populations are exposed to low to moderate levels of arsenic of parts per billion (ppb) to hundreds of ppb. As a consequence, the World Health Organization (WHO) and U.S. environmental health agencies, such as the Environmental Protection Agency (EPA) made arsenic their highest priority. Recently, the WHO, European Union (EU), and US. EPA lowered an acceptable level of 10 ppb for arsenic in drinking water In this article, various health effects of arsenic in drinking water were reviewed and the current status for risk assessment to regulate arsenic in drinking water was discussed.

• 한국환경보건학회지
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• 제49권5호
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• pp.237-246
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• 2023

Background: Arsenic is a metalloid of public health significance due to its unique material properties and toxicity and the widespread pollution in the environment. Arsenic exists as inorganic arsenic and organic arsenic with distinct chemical properties. Its toxicity varies depending on the properties. Objectives: Although the carcinogenicity of arsenic has been identified, the various diseases that occur after acute and chronic exposure to arsenic are not yet clearly known. Methods: Research on the effects of chronic exposure to arsenic on human health was searched and the results were summarized. Results: It has been found that cancer occurs due to exposure to high concentrations of arsenic in areas with elevated exposure to arsenic, but research results have recently been presented on health effects caused by chronic exposure to low concentrations of arsenic. Cancers have also been identified to be related to inorganic arsenic, including skin cancer, lung cancer, and bladder cancer. Significant relationships with neurological diseases, cardiovascular diseases, and diabetes mellitus have been suggested as well. Conclusions: Our results suggest that it is necessary to evaluate the health impact on residents around abandoned metal mines and industrial complexes in South Korea.

• 자원환경지질
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• 제38권1호
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• pp.23-31
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• 2005

본 연구는 이성분계의 화학종 모델링과 삼성분계의 흡착 모델링으로부터 As(III)와 As(V)의 적철석 표면 흡착에 휴 믹산의 영향과 그 결합기작을 고찰하였다. 비소와 휴믹산의 유기 결합의 모델링은 음이온 사이의 정전기적인 반발력 과 비소의 유기 결합을 위한 결합금속의 영향을 고려한 결합 모델이 적합하였다. 삼성분계의 흡착 실험 자료와 비교 할 때 이성분계의 고유상수를 사용한 음이온 경쟁 모델이 음이온 경쟁에 따른 비소의 흡착량과 일치하였다. 반면, 비 소의 유기 결합량의 감소와 휴믹산과의 음이온 흡착경쟁이 흡착량을 감소시키기 때문에 단순합모델은 양이온 중금속 과는 반대로 모델의 편차를 보였다. 반응 기작의 관점에서 휴믹산의 공존하에 비소 유기결합 화학종과 중성화학종의 As(III) 및 음이온의 As(V)가 속착물을 형성하며, 경쟁적으로 적철석 표면으로 이동하여 흡착하게 된다.

• Toxicological Research
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• 제24권3호
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• pp.161-167
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• 2008

Recently, arsenic-toxicity has become the major focus of strenuous assessment and dynamic research from the academy and regulatory agency. To elucidate the cause and the mechanism underlying the serious adverse health effects from chronic ingestion of arsenic-contaminated drinking water, numerous studies have been directed on the investigation of arsenic-toxicity using various in vitro as well as in vivo systems. Neverthless, some questions for arsenic effects remain unexplained, reflecting the contribution of unknown factors to the manifestation of arsenic-toxicity. Interestingly, very recent studies on arsenic metabolites have discovered that trivalent methylated arsenicals show stronger cytotoxic and genotoxic potentials than inorganic arsenic or pentavalent metabolites, arguing that these metabolites could play a key role in arsenic-associated disorders. In this review, recent progress and literatures are summarized on the metabolism of trivalent methylated metabolites and their toxicity on body systems including cardiovascular system in an effort to provide an insight into the future research on arsenic-associated disorders.

• 한국환경과학회지
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• 제28권1호
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• pp.99-106
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• 2019

Arsenic is among the heavy metals commonly found in aqueous environments. Iron oxide is known as an efficient adsorbent for the arsenic. A new synthetic method was applied to provide iron oxide giving a large specific surface area. The mixing method affects the formation of iron oxide. Ultrasonic waves assisted the formation of very fine iron oxide in an organic phase. The synthesized iron oxide is amorphous type with a high surface area of more than $181.3m^2/g$. Sorption capacity of the synthesized adsorbent was relatively very high for arsenic and varied depending on the oxidation state of arsenic: a higher capacity was obtained with As(V). Lower solution pH provided a higher sorption capacity for As(V). The competitive effect of co-exist anions such as chloride, nitrate, and sulfate was minimal in sorption capacity of the iron oxide for arsenic.

• 유기물자원화
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• 제19권1호
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• pp.79-85
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• 2011

솔잎의 기능기를 변형한 인산화 솔잎을 이용한 비소 제거에 관한 연구가 수행되었다. 인산화 솔잎의 표면 상태는 FT-IR, SEM(Scanning Electron Microscopy) 그리고 EDX(Energy Dispersive X-ray)을 이용하여 확인하였다. 비소의 제거율은 pH 7에서 약 98%로 가장 높았다. 또한 대부분의 흡착은 교반 후 30분 내에 이루어 졌으며 비소 이온 용액의 pH는 약 pH 6.5에서 pH 2.4로 시간에 따라 감소하였다.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2004년도 총회 및 춘계학술발표회
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• pp.318-322
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• 2004

Arsenic is a toxic and carcinogenic metalloid, whose sources in nature include mineral dissolution and volcanic eruption. Abandoned mines and hazardous waste disposal sites are another major source of arsenic contamination of soil and aquatic systems. To predict concentrations of the toxic inorganic arsenic in aqueous phase. the biogeochemical redox processes and transport behavior need to be studied together and be coupled in a reactive transport model. A new reaction module describing the fate and transport of inorganic arsenic species (As(II)), dissolved oxygen, nitrate, ferrous iron, sulfate, and dissolved organic carbon are developed and incorporated into the RT3D code.