• 검색 결과가 없습니다.

Evaluation of CH3I Removal Performance and Physical Characteristics for New TEDA Impregnated Activated Carbon Stored in Nuclear Power Plants

N/A
N/A
Protected

Academic year: 2021

Share "Evaluation of CH3I Removal Performance and Physical Characteristics for New TEDA Impregnated Activated Carbon Stored in Nuclear Power Plants"

Copied!
2
0
0

로드 중.... (전체 텍스트 보기)

전체 글

(1)

2019 ⦽ǎႊᔍᖒ⠱ʑྜྷ⦺⫭ ⇹ĥ⦺ᚁݡ⫭ םྙ᫵᧞Ḳ

351

Evaluation of CH3I Removal Performance and Physical Characteristics

for New TEDA Impregnated Activated Carbon Stored in Nuclear Power Plants

Hak-Soo Kim* and Cho-Rong Kim

KHNP Central Research Institute, 70, Yuseong-daero 1312beon-gil, Yuseong-gu, Daejeon, Republic of Korea *[email protected]

1. Introduction

Air Cleaning Unit (ACU) in Nuclear Power Plant (NPP) is adopted to remove radioactive waste as well as toxic materials from operation and accidents. Absorber in ACU is filled with Tri-Ethylene-Di-Amine impregnated activated carbon (TEDA-AC) and has been chosen as an absorbent to remove the radioiodine during normal operation and accident conditions. The CH3I removal performance of

TEDA-AC is affected by the environment factors such as temperature, humidity and toxic materials and should satisfy Regulatory Guide 1.52 for Safety-Related-System and Regulatory Guide 1.140 for Non-Safety-Related-System. But there are only quality assurance requirements for packaging, storage and handling for new TEDA-AC in storage [1]. The performance of new TEDA-AC may be deteriorated due to the environment conditions in storage areas. In this paper, the analysis results of CH3I removal performance, physical characteristics

and TEDA loss for new TEDA-AC according to the storage period are introduced.

2. Representative Sample Selection and

TEDA-AC Storage Conditions

In order to evaluate the CH3I removal performance,

physical characteristics and TEDA loss of new TEDA-AC under storage, representative samples

were selected according to storage period. Table 1 shows the storage period for new TEDA-AC.

Table 1. Storage Period for New TEDA-AC

NPP Purchase Date Sampling Date Storage Period NPP 1 2016-07 2017-06 < 1 year (11 months) NPP 2 2012-04 2017-03 < 5 year (59 months) NPP 3 2011-06 2017-07 > 5year (73 months)

The new TEDA-AC in NPP is packed and stored in according with Level 2 requirements of ASME NQA-1-2015, Subpart 2.2 [1]. The new TEDA-AC is sealed in vinyl and then stored in a sealed drum as shown in Fig. 1.

Fig. 1. Packaging Status of New TEDA-AC.

3. Analysis Results of New TEDA-AC

The CH3I removal performance of new TEDA-AC

was tested according to ASTM D3803-91 [2]. The results are shown in Table 2.

(2)

352

2019 ⦽ǎႊᔍᖒ⠱ʑྜྷ⦺⫭⇹ĥ⦺ᚁݡ⫭םྙ᫵᧞Ḳ Table 2. Analysis Results of CH3I Removal Performance

NPP Samples Results

NPP 1 < 1 year (11 months) 99.785±0.07

NPP 2 < 5 year (59 months) 99.885±0.004

NPP 3 > 5year (73 months) 99.821±0.007

The physical characteristics of new TEDA-AC was analyzed according to ASME AG-1-2015 FF-5120 [3] and its results are shown in Table 3.

Table 3. Analysis Results of Physical Characteristics

Test Items Method Criteria Results < 1 year < 5 year > 5 year Apparent Density D2854 Min. 0.38 g/ຸ 0.57 0.54 0.57 Particle Size Distribution

D2862 Passed Passed Passed ASME E-11 Sieves

-retained on No.6 Max. 0.1% -retained on No.8 Max. 5.0% -No.8 retained on No.12 Max. 60.0% -No.12 retained on No.16 Min. 40.0% -through No.16 Max. 5.0% -through No.18 Max. 1.0%

Moisture Content D2867 Measured 2.3 2.9 3.8 ball-pan hardness D3802 Min. 60.0% 99.6 99.7 99.8

pH D3838 Measured 10.1 10.1 9.7

ACU in NPP use activated carbon with 5% TEDA-AC to remove the radioiodine. It was additionally analyzed whether TEDA loss occurred according to storage period. TEDA loss analysis was performed using a thermal analyzer system and the results of TEDA loss are shown in Fig. 2.

( < 1 year)

( < 5 year)

(> 5 year)

Fig. 2. Analysis Results of TEDA Loss.

4. Conclusion

The new TEDA-AC is stored in warehouse for long-term periods before being installed in ACU. The results of the analysis showed that there was no significant change in the CH3I removal performance

and physical characteristics of new TEDA-AC after long-term storage.

REFERENCES

>@ $60( ³4XDOLW\ $VVXUDQFH 5HTXLUHPHQWV IRU 1XFOHDU )DFLOLW\ $SSOLFDWLRQV´ $60( 14$-1-2015, Subpart 2.2, New York, NY.

[2] ASTM, ³6WDQGDUG7HVW0HWKRGIRU1XFOHDU-Grade $FWLYDWHG&DUERQ´$670'-91, 2014. [3] ASME, ³&RGHRQ1XFOHDU$LUDQG*DV7UHDWPHQW

Article FF-,QVSHFWLRQDQG7HVWLQJ´$60( AG-1-2015, 2015.

수치

Fig. 1. Packaging Status of New TEDA-AC.
Table 3. Analysis Results of Physical Characteristics

참조

관련 문서

That is, the dry powder of the sludge wastes, generated during the decommissioning of nuclear power plants, were compacted, and a study, focused on

How to strengthening safety assessment capability for design and operation of nuclear power plants. ● Opening

Waste lubricating oil, which is radioactive waste generated from nuclear power plants, is a lubricant for major equipment of nuclear power plants, and is incinerated

In nuclear power plants, the water level is maintained by controlling the water supply when the steam generator's water level deviation occurs. During

In an effort to develop a new method to remove nitrogen, this study examined the effects of C/N ratio, carbon source and nitrogen concentration on

In order to remove phosphorus contained in domestic sewage, an experimental investigation is performed using intermittently aerated activated sludge process

Owing to nuclear power plant data characteristics such as nonlinear, time sequential and multivariate, in this light, this thesis aims at proposing an

For example, the public’s sentiments of risk regarding nuclear power plants exceeds the risk felt by an expert in the area, and therefore the public sentiment is a negative