• Title/Summary/Keyword: 먹는 샘물

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지하수 전문기관에 의한 먹는샘물 관리방안

  • Lee Byeong-Dae;Seong Ik-Hwan;Kim Jeong-Suk;Im Hyeon-Cheol;Kim Yong-Je
    • Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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    • 2005.04a
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    • pp.65-67
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    • 2005
  • 먹는물 관리법 제19조의2 제2항에서 환경부장관은 지하수 전문기관을 지정하여 먹는샘물제조업자로부터 제출받은 수질측정결과를 지하수 전문기관으로 하여금 분석하도록 하는 먹는샘물 사후관리를 규정하고 있다. 그러므로 지하수 전문기관은 먹는샘물의 수량 수질자료에 대한정보의 수집 분석 및 관리와 먹는샘물 통합관리시스템 개발 및 구축, 먹는샘물 제조업체의 현장시설관리 등 사후관리 기능을 지속적으로 수행해야 한다.

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먹는 생물과 미생물학적 품질

  • Cha, Seong-Gwan
    • Bulletin of Food Technology
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    • v.8 no.2
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    • pp.20-26
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    • 1995
  • 건강한 성인 한사람은 하루에 약 $3\ell$의 물을 외부로부터 섭취하여야 한다고 한다. 이중 약 $1-2\ell$의 물은 음료 즉, 먹는물의 형태로 외부로부터 섭취하게 되는데, 이러한 음료의 형태로 섭취되는 먹는 물이 우리의 건강을 좌우하게 된다는, 물은 많이 마실수록 건강에 좋고, 깨끗한 생수를 마시는 것이 건강의 비결이라는 말을 많이 듣게 된다. 또 환경오염으로 인한 식수의 오염문제가 심각하게 대두되고 있어 많은 사람들은 오염되지 않은 깨끗한 물, 생수 등을 찾고 있는 실정이다. 이러한 한국의 현실에서 1995. 5. 1. 부터 환경부의 "먹는물 관리법"이 새롭게 시행되기 시작하여 지금까지 사용되어오던 "광천음료수"가 "먹는샘물"이라는 용어로 변경이 되고 몇가지 품질규격에 있어 더욱 엄격하게 규제가 되기 시작하였다. 따라서 새롭게 시작되는 "먹는물 관리법"의 "먹는샘물"의 정의와 먹는샘물의 미생물학적인 품질의 설명이 필요하고, 또 "먹는물", "먹는샘물"이 환경쪽에서만 다루어야 할 문제가 아니라 먹는 물은 항상 식품과 함께 취급되기 때문에 식품연구의 일환으로서도 취급되어져야 함을 강조하고자 이글을 쓰게 되었다.

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포장과 법률 - '먹는샘물 등의 기준과 규격 및 표시기준 고시' 일부개정령(안) 행정예고

  • (사)한국포장협회
    • The monthly packaging world
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    • s.329
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    • pp.96-99
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    • 2020
  • 환경부는 지난 8월 19일 플라스틱의 재활용률을 높이고 발생량 저감을 유도하기 위해 먹는샘물 용기에 부착하던 표시사항(라벨)을 병마개에 부착을 허용하는 등 현행제도 운영상 미흡한 부분들을 개선·보완하기 위해 '먹는샘물 등의 기준과 규격 및 표시기준 고시' 일부개정령(안)을 행정예고했다. 다음에 그 주요내용에 대해 살펴보도록 한다.

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Speculation on the Water Quality for the Natural Mineral Water (국내 먹는샘물의 특정 수질 항목에 대한 고찰)

  • 조병욱;이병대;이인호;추창오
    • The Journal of Engineering Geology
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    • v.12 no.4
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    • pp.395-404
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    • 2002
  • Contents of the specific components in the natural mineral water was discussed in relation to the well depth and geology. According to water quality data during the last five years(1998~2002), the nitrate and fluoride concentrations, and pH averaged 0.89~ 1.09 mg/L, 0.37~0.45 mg/L, and 7.30~7.59, respectively. These values are the similar range to those of generalized groundwater having same well depths, implying that shallow groundwaters flow into the production wells. In general, no clear relationships between the water quality, well depth, and geology were found. The average arsenic concentration of the natural mineral water increased from 0.0024 mg/L in 1999 to 0.0066 mg/L in 2002. The percentage of production well with arsenic level higher than 0.001 mg/L also increased from 20.1% in 1999 to 64.9% in 2002. In 2002, 11 out of 57 production wells exceed 0.001 mg/L which will be announced as a new arsenic standard for drinking water by USEPA.

Determination of bromide in bottled mineral water and ground water in Korea (먹는 샘물 및 지하수 원수 중 bromide 분석연구)

  • Ahn, Hye-Sil;Seo, Kyoung-Ae;Park, Ju-Hyun;Lee, Jun-Bae;Kim, Tae-Seung;Han, Jin-Seok;Kwon, Oh-Sang
    • Analytical Science and Technology
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    • v.24 no.1
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    • pp.10-14
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    • 2011
  • This study was performed to compare international analytical methods of bromide and applied to determine bromide in bottled mineral water and raw ground water in Korea. Bromide in water was eluted by 10~50 mM potassium hydroxide (KOH) and determined by ion chromatography-suppressed conductivity detector (IC-CD). Sample was purified with Ba- and H-on-guard cartridge and $0.2\;{\mu}m$ membrane filter. The method detection limit (MDL) and the limit of quantitation (LOQ) of bromide were 0.2 and $0.5\;{\mu}g/L$, respectively. The calibration curve showed good lineality above 0.9993 in the ranges of the $0.5\sim80\;{\mu}g/L$. A correlation coefficient of bromide in ground water and sum of bromide and bromate in bottled mineral water is 0.808.

Quantitation of Phthalate and Adipate in Natural Mineral Water and PET Container (먹는 샘물 및 PET 용기 중 Phthalate와 Adipate의 정량분석)

  • Shin, Ueon-Sang;Ahn, Hye-Sil;Shin, Ho-Sang
    • Analytical Science and Technology
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    • v.15 no.5
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    • pp.475-481
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    • 2002
  • The determination of phthalates and adipate in natural mineral water and its container is described. Phthalates and adipate were extracted from natural mineral water by liquid-liquid extraction with methylene chloride, concentrated and then injected in GC-MS (SIM). Phthalates and adipate from 1) PET, cap, label and glue were extracted in Soxhlet with 50 mL of carbon tetrachloride, purified with silicagel and detected with GC-MS (SIM). Peak shapes and quantitation of phthalates and adipate were excellent, with linear calibration curves over a range of $0.1{\sim}10{\mu}g/L$ in water sample ($r^2$ > 0.996) and over a range of $1{\sim}1,000{\mu}g/Kg$ in solid samples ($r^2$>0.994). The detection limits of analytes were $0.002{\sim}0.010{\mu}g/L$ in water and $0.01{\sim}0.02{\mu}g/Kg$ in solid samples. Five kinds of natural mineral water samples, two PETs, two labels, two caps and two glues were quantified by the described procedure. As a results, the concentrations of total phthalates in natural mineral water ranged from ND ~ 1.2 ng/mL. Otherwise, the concentrations of total phthalate extracted from PET ranged from 0.55 ~ 1.2 mg/Kg. We found that the accurate determination of phthalte and adipate in natural mineral water and container must be considered blank correction and the removal of label and glue in PET sample.

Current Situation and Problems in Applying Groundwater Flow Models to EIAs in Korea (지하수환경영향예측을 위한 지하수모델의 적용현황 및 문제점: 환경영향평가서와 먹는샘물환경영향조사서를 중심으로)

  • 김강주
    • Journal of the Korean Society of Groundwater Environment
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    • v.6 no.2
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    • pp.66-75
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    • 1999
  • This work was initiated to investigate current situation and problems in applying groundwater-related models for various kinds of environmental impact assessment in Korea. and therefore. to enhance appropriate application in the future. This study was carried out with 544 and 16 documents of EIA (Environmental Impact Assessment. Law of Environmental Impact Assessment) and Mineral-Water EIA (“the environmental impact investigation for mineral water developments”; Law of Drinking Water Management). respectively. It was revealed that there were considerably many cases which may cause serious impacts on subsurface environments in EIA. However. none applied groundwater models. Generally, the influences on subsurface system were underestimated or even ignored in EIA. For Mineral-Water EIA. groundwater models wert applied. in general. But. numerous and serious problems were noted: limited number of calibration parameters and parameter types. setting boundary conditions without adequate bases. recharge rates several times higher than precipitation rates. numerically unstable results. etc. Such kinds of misusages seem to be caused by modelers larking in professional knowledges. To solve the problems revealed from this study. more systematic re-education programs are suggested.

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