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Chapter 6 Radiation Control

With commissioning of the Low-Level Radioactive Waste Disposal Center of the Japan Nuclear Fuel Development Co., transfer of homogeneous solidified radioactive waste packages (concentrated liquid waste packages) and solidified radioactive waste packages with filler (solidified miscellaneous solid waste with mortar etc. in the drum) from NPPs to the Center started in 1992 and 2000, respectively. "Hie total number of packages sent to the Center is shown in Figure 6.8.3.

In manufacturing a solidified radioactive waste package with filler, as measures to increase packing efficiency of miscellaneous solid waste into a drum, high pressure compression processing and melt processing (high frequency induction heating and plasma melting) have been introduced. Therefore, as more miscellaneous solid waste will be taken from NPPs at an increasing rate from now on, the amount of solid waste stored at them is expected to decrease.

Figure 6.8.4 provides an outline of the Low-Level Radioactive Waste Disposal Center of the Japan Nuclear Fuel Development Co. Disposal methods of the radioactive solid waste generated from NPPs are provided in Table 6.8.1.

Beginning with the above-mentioned disposal of low level radioactive waste, the system to dispose radioactive wastes according to the radioactivity level has been promoted, and in 2005, the legislation related to the clearance system (radioactive wastes of very low radioactivity level for which the effect on human health can be ignored, may be reused or disposed as general industrial wastes) was revised. An actual application of the new clearance system has just been started for the decommissioning of the Tokai Nuclear Power Plant of Tokai Daiichi Power Station of the Japan Atomic Power Company Co. Ltd. From now on, it will be applied to the waste generated at light water reactors.

Figure 6.8.5 shows an outline of the clearance system.

  1. Radioactive liquid Wastes

light water NPPs generate liquid wastes coming from pumps or valves gland seals, rinse water of facilities and equipment, liquid waste generated by recycling of ion exchange resin, and liquid waste from laundry and restrooms, etc. The water coming

from these sources is purified and reused as much as possible by filtering, desalination (removal of radioactive materials with ion exchange resin), and/or condensation, etc. by dedicated treatment facilities according to the conductivity, solid content, radioactivity concentration, etc. Moreover, when the wastes are to be discharged to the environment, they are stored in dedicated tanks, the radioactivity is measured, and the discharge is controlled so as not to exceed the concentration limits provided by law and not to exceed the amount of discharge for achieving the target value (50 pSv/year). These measures ensure the dose received by the general public is low (annual discharge control target).

Figure 6.8.6 shows the trends for discharged radioactivity of radioactive liquid wastes (excluding tritium).

Although radioactive materials exceeding the radioactivity of 1010 Bq/year were released at the beginning, improvements of fuel integrity and water quality of the primary system coolant, introduction of low cobalt-containing materials and corrosion resistant materials (reduction of activation product generation), improvement in performance of clean­up systems, reduction of drainage generated, improvement of washing method, etc. have resulted in a downward tendency every year. Further, since 1996, it has mainly been under the detection limit

Figure 6.8.7 shows the tritium (’H) discharge record. It has been mostly flattening out in recent years, but the discharge from PWRs is one order of magnitude higher than that from BWRs. Ulis is because boron is added to the PWR reactor water for power level control, which generates tritium by the boron and neutron reaction. Tritium emits only beta rays of very low energy and cannot be removed by condensation as it is included in water molecules. But, since it is not enriched in the human body and also the degree of dose contribution is low, the discharge control limit is specified under a different classification so that the discharge control target is different from that of “Co and other radionuclides.

6 25

NSRA, Japan

Waste Processing Method at Nuclear Power Stations

Nuclear power station

(P^R-type) £^4

| tank r

(BWR-type)

Filter

Measure k J1

»t concentration of 1-1

*1 radioactive Discharge from stack

. materials to

H ensure safety

Liquid

Activated carbon type rare gas hold-iip equipment Filter

(Decay concentration of radioactive materials)

.... ,dn ■ Ventilation of t s

Filter- Filter NPS buildings y Reuse

N ucle at p ower station

Nuclear power station

V .Filtration and

demoralization Demineralizer

H (Distilled water! y

- Concentrated liquid waste -Evaporationconcentration"

Materials not requiring ” y

treatment as radioactive wastes

Measure concentration of radioactive materials to

> , ensure safety

Discharge to ocean

The same repository treatment as industrial wastes

Low -level radioactive waste (Concrete Very low radioactive wastes Metal etc.)

Reuse

Paper, cloth etc.

Solid hjW turning, compressing etc - q

. —' ' Drum. ij

Used, flit er. sludee.

Low level radioactive waste

Nuclear power station

E

laterilas of comparatively low adioactive material concentration

Burial treatement

Solidify in

container

(Store in the Low level radioactive waste

site safely) Materilas of comparatively high.

radioactive material concentration

ion exchange resin f . $

° Storage tank ,h

Reduce concentration of h radioactive materials

Activated metal

(Control rod & Cutting ■

core internals) (Store in the site) s Solidification Underground repository disposal

e c’ (Store in the

site safely) Source; Agency of Natural Resources and Energy "2005

Figure 6.8 J Processing methods of radioactive waste at NPPs

Repository disposal into concrete vault

IRS 50-100m

Mt below ground