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Weapons of Mass Destruction (WMD)

I.11.0 RADIOLOGICAL ENVIRONMENT: OVERVIEW AND POTENTIAL RADIATION DOSES FROM 1994 HANFORD SITE OPERATIONS

This section provides a brief introduction to the subject of radioactivity and to some of the common terms used in radiological health evaluation. It also summarizes 1994 data on radiation doses from operations at the Hanford Site and estimates the potential future fatal cancers attributable to these radiation exposures.

I.11.1 INTRODUCTION TO RADIOACTIVITY

Radioactivity is a broad term that refers to changes in the nuclei of atoms that release radiation. Radiation is an energetic ray or energetic particle. For ionizing radiation, the ray or particle has enough energy to cause changes in the chemical structure of the materials it strikes. These chemical structure changes are the mechanisms by which radiation can cause biological damage to humans.

Radiation comes from many sources, some natural and some man-made. People have always been exposed to natural or background radiation. Natural sources of radiation include the sun, and radioactive materials present in the earth's crust, in building materials and in the air, food, and water. Natural radioactivity can even be found within the human body. Some sources of ionizing radiation have been created by people for various uses or as by products of these activities. These sources include nuclear power generation, medical diagnosis and treatment, and nuclear materials related to nuclear weapons.

Radioactive waste is a result of the use and production of radioactive materials. At the Hanford Site, DOE manages radioactive waste that was generated primarily by the production of plutonium for nuclear weapons. These waste is classified as low-activity, high-level, or transuranic. When radioactive waste is combined with hazardous chemical wastes, it is referred to as mixed waste. High-level waste is the most dangerous type of radioactive waste and requires extensive shielding by materials such as lead and concrete and special handling. Transuranic waste is material contaminated with radioactive elements heavier than U. While long lasting, transuranic waste does not require the same degree of isolation as high-level waste. Low-activity waste is generally the least dangerous type of radioactive waste and requires fewer measures to isolate it from people and the environment. Depending on the particular radioactive material involved, radioactive waste can be harmful and thus require isolation for up to hundreds or even thousands of years. Plutonium-contaminated waste will be radioactive for thousands of years. Radioactive Cs, on the other hand, will be virtually gone in 250 years.

I.11.2 COMMON TERMS IN RADIOLOGICAL HEALTH EVALUATIONS

Radiation dose to individuals is usually expressed in rem or millirem (mrem), which is one-thousandth of a rem. The rem is a measure of the biological effects of ionizing radiation on people. It is estimated that the average individual in the United States receives an annual dose of about 300 millirem from all natural sources. The collective radiation dose to a population is termed the person-rem, which is calculated by adding up the radioactive dose to each member of the population.

Any dose of radiation can damage body cells. However, at low levels, such as are received from a medical x-ray, the damage to cells is so slight that the cells can usually repair themselves or can be replaced by the regeneration of healthy cells. Radiation exposures are often classified as acute (a dose received over a short time) or chronic (a dose received over a long time). Chronic doses are usually less harmful than acute doses because the body has time to repair or replace damaged cells; however, even low doses can have harmful effects.

Impacts from radiation exposure often is expressed using the concept of risk. The most substantial radiation-related risk is the potential for developing cancers that may cause death in later years. This delayed effect is measured in latent (future) cancer fatalities. The risk of a latent cancer fatality is estimated by converting radiation doses into possible numbers of cancer fatalities. For an entire exposed population group, the latent cancer fatality numerical value is the chance that someone in that group would develop an additional cancer fatality in the future because of the radiation exposure, (i.e., a cancer fatality that otherwise would not occur).

Radiological risk evaluations often refer to the maximally-exposed individual. This would be the member of the pubic or a worker who receives the highest possible dose in a given situation. As a practical matter, the maximally-exposed individual likely would be a person working with radiological or hazardous materials.

I.11.3 POTENTIAL RADIATION DOSES AND LATENT CANCER FATALITIES FROM 1995 HANFORD SITE OPERATIONS

Each year potential radiation doses to the public are calculated for exposure to Hanford Site effluents. The 1995 information presented here was taken from the Hanford Site Environmental Report for calendar year 1995 (PNL 1996 ). Doses are calculated from reported effluent releases, from environmental surveillance results, and from information about operations at specific Hanford Site facilities.

The 1995 potential dose from Hanford Site operations to the hypothetical maximally-exposed individual member of the public was 0.02 mrem , compared to 0.05 mrem reported for 1994 (PNL 1996) . The current DOE radiation dose limit for an individual member of the public is 100 mrem per year, and as stated previously, the national average dose from natural sources is 300 mrem per year. Thus, the maximally-exposed individual potentially received a small fraction of 1 percent of both the DOE dose limit and the natural background average dose.

The total population of the surrounding area (380,000 persons) received a potential dose from 1995 Hanford Site operations of 0.3 person-rem. The 1994 average dose to an individual member of the public was 0.0009 mrem. This is 0.001 percent of the 100 mrem/year standard and 0.0003 percent of the 300 mrem per year received from typical natural sources. Clean Air Act requirements specify a maximum radiation dose through the air of 10 mrem per year. The 1995 air emissions from the Hanford Site were 0.006 mrem, which is less than 0.1 percent of the 10 mrem standard.

Based on a dose-to-risk conversion of 0.0005 latent cancer fatalities per rem (each rem equates to 0.0005 latent cancer fatalities), there would be 0.0001 latent cancer fatalities in the general public attributable to exposure to effluents from 1995 Hanford Site operations.

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