ML20215G149: Difference between revisions

From kanterella
Jump to navigation Jump to search
(StriderTol Bot insert)
 
(StriderTol Bot change)
 
Line 17: Line 17:


=Text=
=Text=
{{#Wiki_filter:l h:'     .
{{#Wiki_filter:l h:'
i i
i i
    *
MAXIMUM
* MAXIMUM
* OFF-SITE DOSES AND DOSE COMMITMENTS TO MEMBERS OF'THE PUBLIC Dose, M1111 rems Source 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Year **
* OFF-SITE DOSES AND DOSE COMMITMENTS TO MEMBERS OF'THE PUBLIC Dose, M1111 rems Source                       1st Qtr   2nd Qtr     3rd Qtr   4th Qtr     Year **
Note:
Note:                                                           l
l
                                                                              +
+
Organ               BONE       LIV       LIV       .GI         GI Liquid Effluents (1)         4.4E-02   2.7E-02''1.0E-02     9.9E-02,.144E-01 Airborne Effluents                           s Sector               SW         W         SW         'SW         SW Iodines &             4.3E-03   1.6E-03     2.5E-03   1.3E-02     2.1E-02 Particulates         (2)
Organ BONE LIV LIV
Sector               WFW         S         W         WSW       WSW Noble   gases       (3)     4.5E-03   3.0E-03     3.9E-03   1.4E-02     2.4E-02 Sector               NE         E         E         NE         NE Direct Radiation (4)         2.7E 01   2.8E 01     2.5E 01   2.7E 01     9.0E 01
.GI GI Liquid Effluents (1) 4.4E-02 2.7E-02''1.0E-02 9.9E-02,.144E-01 Airborne Effluents s
                  *" Maximum"   means   the   largest   fraction   of   the   corresponding 10CFR50 Appendix I dose design objective.
Sector SW W
                  **" Maximum" dose   for   the   year may not equal the sum of the quarterly maximum doses because the doses may be to different organs or may occur at different places.
SW
Notes                                                                                 l
'SW SW Iodines &
: 1. The     liquid effluent total body and organ doses are determined primarily by the fish pathway. These are calculated using the bioaccumulation       factors ,    dose conversion factors and assumptions of Regulatory guide 1.109 (March 1976).
4.3E-03 1.6E-03 2.5E-03 1.3E-02 2.1E-02 Particulates (2)
: 2. Airborne effluent iodine and particulate doses are determined through the inhalation pathway using reported isotopic con-                   ,
Sector WFW S
centrations, atmospheric dispersion assumptions of Regulatory i
W WSW WSW Noble gases (3) 4.5E-03 3.0E-03 3.9E-03 1.4E-02 2.4E-02 Sector NE E
guide 1.111     (March 1976)     and inhalation dose factors of               j Regulatory   guide   1.109. Once   calculated     these doses are multiplied by a constant (230) to convert them to the grass / cow /
E NE NE Direct Radiation (4) 2.7E 01 2.8E 01 2.5E 01 2.7E 01 9.0E 01
*" Maximum" means the largest fraction of the corresponding 10CFR50 Appendix I dose design objective.
**" Maximum" dose for the year may not equal the sum of the quarterly maximum doses because the doses may be to different organs or may occur at different places.
Notes l
: 1. The liquid effluent total body and organ doses are determined primarily by the fish pathway.
These are calculated using the bioaccumulation factors dose conversion factors and assumptions of Regulatory guide 1.109 (March 1976).
: 2. Airborne effluent iodine and particulate doses are determined through the inhalation pathway using reported isotopic con-centrations, atmospheric dispersion assumptions of Regulatory i
guide 1.111 (March 1976) and inhalation dose factors of j
Regulatory guide 1.109.
Once calculated these doses are multiplied by a constant (230) to convert them to the grass / cow /
milk pathway equivalents in accordance with the OFFSITE DOSE CALCULATION MANUAL (ODCM).
milk pathway equivalents in accordance with the OFFSITE DOSE CALCULATION MANUAL (ODCM).
: 3. The noble gas doses are determined using the measured isotopic concentrations, the atmospheric           dispersion     assumptions of Regulatory guide 1.111 and submersion         dose factors       from Reg-ulatory guide 1.109.
: 3. The noble gas doses are determined using the measured isotopic concentrations, the atmospheric dispersion assumptions of Regulatory guide 1.111 and submersion dose factors from Reg-ulatory guide 1.109.
: 4. Direct radiation was assessed using thermal luminescent dos-imetry. Two dosimeters containing three LiF TLD chips each were placed at selected locations within each of 16 sectors around the plant. These chips were collected and read quarterly and annually.
4.
i 0706230138 8706 PDR    ADOCK 05000 48 PDR                                        Miended May 8, 1987 R
Direct radiation was assessed using thermal luminescent dos-imetry.
Two dosimeters containing three LiF TLD chips each were placed at selected locations within each of 16 sectors around the plant. These chips were collected and read quarterly and annually.
i 0706230138 8706 ADOCK 05000 48 Miended May 8, 1987 PDR PDR R
J}}
J}}

Latest revision as of 22:25, 3 December 2024

Errata to Semiannual Radioactive Effluent Release Rept for Jul-Dec 1986, Correcting Direct Radiation Results from Sectors at the Site Boundaries
ML20215G149
Person / Time
Site: Farley  Southern Nuclear icon.png
Issue date: 12/31/1986
From:
ALABAMA POWER CO.
To:
Shared Package
ML20215G121 List:
References
NUDOCS 8706230138
Download: ML20215G149 (1)
v • d • e


Text

l h:'

i i

MAXIMUM

  • OFF-SITE DOSES AND DOSE COMMITMENTS TO MEMBERS OF'THE PUBLIC Dose, M1111 rems Source 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Year **

Note:

l

+

Organ BONE LIV LIV

.GI GI Liquid Effluents (1) 4.4E-02 2.7E-021.0E-02 9.9E-02,.144E-01 Airborne Effluents s

Sector SW W

SW

'SW SW Iodines &

4.3E-03 1.6E-03 2.5E-03 1.3E-02 2.1E-02 Particulates (2)

Sector WFW S

W WSW WSW Noble gases (3) 4.5E-03 3.0E-03 3.9E-03 1.4E-02 2.4E-02 Sector NE E

E NE NE Direct Radiation (4) 2.7E 01 2.8E 01 2.5E 01 2.7E 01 9.0E 01

  • " Maximum" means the largest fraction of the corresponding 10CFR50 Appendix I dose design objective.
    • " Maximum" dose for the year may not equal the sum of the quarterly maximum doses because the doses may be to different organs or may occur at different places.

Notes l

1. The liquid effluent total body and organ doses are determined primarily by the fish pathway.

These are calculated using the bioaccumulation factors dose conversion factors and assumptions of Regulatory guide 1.109 (March 1976).

2. Airborne effluent iodine and particulate doses are determined through the inhalation pathway using reported isotopic con-centrations, atmospheric dispersion assumptions of Regulatory i

guide 1.111 (March 1976) and inhalation dose factors of j

Regulatory guide 1.109.

Once calculated these doses are multiplied by a constant (230) to convert them to the grass / cow /

milk pathway equivalents in accordance with the OFFSITE DOSE CALCULATION MANUAL (ODCM).

3. The noble gas doses are determined using the measured isotopic concentrations, the atmospheric dispersion assumptions of Regulatory guide 1.111 and submersion dose factors from Reg-ulatory guide 1.109.

4.

Direct radiation was assessed using thermal luminescent dos-imetry.

Two dosimeters containing three LiF TLD chips each were placed at selected locations within each of 16 sectors around the plant. These chips were collected and read quarterly and annually.

i 0706230138 8706 ADOCK 05000 48 Miended May 8, 1987 PDR PDR R

J

Retrieved from "https://kanterella.com/w/index.php?title=ML20215G149&oldid=3977160"