radon Ölçüm teknikleri

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    Radon Measurement Devices

    Long-Term Measurements

    Short-Term Measurements

    Sampling Methods

    Passive Devices

    Active Devices

    Radon Measurement

    Radon Measurement Techniques

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    Passive Devices

    Passive radon testing devices do not need power to function. These

    include charcoal canisters, alpha-track detectors, charcoal liquid

    scintillation devices, and electret ion chamber detectors which are

    available in hardware, drug, and other stores; they can also be ordered by

    mail or phone. These devices are exposed to the air in the home for a

    specified period of time and then sent to a laboratory for analysis. Bothshort-term and long-term passive devices are generally inexpensive.

    Some of these devices may have features that offer more resistance to

    test interference or disturbance than other passive devices. Qualified

    radon testers may use any of these devices to measure the home's radon

    level.

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    Active Devices

    Active radon testing devices require power to function. These include

    continuous radon monitors and continuous working level

    monitors. They continuously measure and record the amount of radon

    or its decay products in the air. Many of these devices provide a report of

    this information which can reveal any unusual or abnormal swings in theradon level during the test period. A qualified tester can explain this

    report to you. In addition, some of these devices are specifically

    designed to deter and detect test interference. Some technically

    advanced active devices offer anti-interference features. Although these

    tests may cost more, they may ensure a more reliable result.

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    Radon Measurement Techniques

    There are several radon measurement devices that may be used to

    test a home or building for radon.

    These devices fall into two broad categories: those used forlong-term

    measurements (testing period of 3 to 12 months in duration) or those

    designed forshort-term measurements (testing period of less than 3months and more typically 2 to 7 days).

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    Long-Term

    Measurements

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    Alpha Track Detector

    These detectors use a small piece of special plastic or film inside acontainer with a filter-covered opening. Air being tested diffuses

    (passive detector) or is pumped (active detector) through a filter

    covering a hole in the container. When alpha particles from radon and

    its decay products strike the detector, they cause damage tracks. At the

    end of the test period the container is sealed and returned to alaboratory for reading. The radon exposure duration of an alpha track

    detector is usually 1 to 12 months.

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    Electret Ion Chamber

    This device consists of a special plastic canister (ion chamber)containing an electrostatically charged disk detector (electret). The

    detector is exposed during the measurement period, allowing radon to

    diffuse through a filter-covered opening into the chamber. Ionization

    resulting from the decay of radon produces a reduction in the charge

    on the electret. The drop in voltage on the electret is related to theradon concentration. The detectors may be read in the home using a

    special analysis device to measure the voltage or mailed to a

    laboratory for analysis. This type of detector may be deployed for 1 to

    12 months.

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    Digital Detector

    This detector plugs into a standard wall outlet much like a consumer

    carbon monoxide detector, and continuously monitors for radon. It is

    a passive device based on an ion chamber. It allows the

    homeowner to make radon measurements in different areas of the

    home. After being plugged in for an initial period of 48 hours, thedevice displays the average radon concentration continuously.

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    Short-TermMeasurements

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    Activated Charcoal Adsorption

    These devices utilize an airtight container filled with activated

    charcoal and covered with a screen and filter. The detector is

    opened in the area to be sampled and exposed to the air for a

    specified period of time. Radon present in the air adsorbs onto the

    charcoal. At the end of the sampling period, the container is sealed

    and then sent to a laboratory for analysis using a scintillation

    detector. Charcoal detectors may be subject to effects from drafts

    and high humidity. These detectors are normally deployed for

    measurement periods of 2 to 7 days.

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    activated charcoal filter element

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    Charcoal Liquid Scintillation

    This method is very similar to the activated charcoal detector in that itemploys a small vial of activated charcoal for sampling the radon.

    Following exposure, the vial is sealed and returned to a laboratory for

    analysis by treating the charcoal with a scintillation fluid, then analyzing

    the fluid using a scintillation counter. These detectors are also deployed

    for normal periods of 2 to 7 days.

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    Electret Ion Chamber

    This is the same device described for long-term tests. However,variations in the design of the electret allows for a short-term

    measurement as well. The short-term electret ion chamber is deployed

    for 2 to 7 days.

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    Continuous Radon Monitoring

    This detection category includes devices that record real-time

    continuous measurements of radon gas over a series of minutes and

    report the results in hourly increments. Air is either pumped or diffuses

    into a counting chamber, typically a scintillation cell or ionization

    chamber. The result using this type of detector is normally available at

    the completion of the test in the home or building without additionalprocessing or analysis. These detectors are normally deployed for a

    minimum of 48 hours.

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    Continuous Working Level Monitoring

    These devices record real-time continuous measurement of theradioactive decay products of radon in the air. Radon decay

    products are sampled by continuously pumping air through a filter.

    Alpha particles from the decay of products trapped on the filter are

    counted to determine the concentration of radon decay products in

    the air sampled. Continuous working level monitors should bedeployed for a minimum of 48 hours.

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    Sampling Methods

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    Grab sampling

    Grab samples consist of essentially instaneous measurements of the radon or

    radon progeny concentration in air over time intervals that are short (on the

    order of minutes) compared to the time scale of fluctuations in concentration.

    The air is collected in a container and brought back to the laboratory for

    analysis. Typical containers include plastic bags, metal cans and glass

    containers. The volumes of the containers are usually between 5 liters and 20

    liters.

    Continuous sampling

    Continuous sampling involves the automatic taking of measurements at closelyspaced time intervals over a long period of time. The result is a series of

    measurements which can give information on the pattern with which the

    concentration varied throughout the measurement interval.

    Integrating Sampling

    Integrating devices collect information on the total number of radition eventswhich occur throughout some fairly long period of time, usually on the order of

    several days to months. The result from integrating devices is an estimate of

    the approximate average concentration through the environment interval.

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    Ev-ii radon konsantrasyonlarnn lmleri pasif yntemle, CR-39

    plastik detektrlerin kullanm ile yaplmtr. Pasif nkleer iz detektr

    olarak doal fon alfa n izlerinin dk olmas nedeniyle, ticari ad CR-

    39 olan alil diglikol karbonat plastik detektrler tercih edilmitir.

    Detektrler zerlerindeki barkot numaralar deftere kaydedilmitir.Radon

    ve bozunma rnlerinin yaynladklar alfa tanecikleri difzyon kaplarnn

    iine girerek detektrle etkilemekte ve detektr yzeyinde gzle

    grlemeyecek byklklerde izler oluturmaktadr.

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    Ev ile ilgili daha ayrntl bilgiye ulamak iin on sorudan oluan bir anket

    uygulanmtr. Detektrler, 60 gn srelerle evlerde bekletilmitir. 60 gnlkgzlem sresi sonunda toplanan detektrler zerindeki alfa izlerinin

    grlebilir hale getirilebilmesi iin kimyasal iz kazma ilemi uygulanmtr.

    Bu ilem iin detektrler otomatik kimyasal iz kazma cihaznda 4 saatlik bir

    kimyasal ileme tabi tutulmaktadr. Daha sonra bilgiyara bal gelimi bir

    mikroskop sistemi ve softwareden oluan otomotik radon iz okuma

    cihaznda 2 er kez okumalar yaplarak aritmetik ortalamalar alnm vekonsantrasyonlar tayin edilmektedir.

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    Otomatik iz okuma sistemi

    Kimyasal iz kazma banyosu