Summary for understanding

12

Transcript of Summary for understanding

Page 1: Summary for understanding

March 2020

Fisheries Agency of Japan

For �

sh co

nsumption with peace of mind

Summary forunderstanding

the monitoring inspectionof radioactive materials

Website of the Fisheries Agency (in English): https://www.jfa.maff.go.jp/e/inspection/index.html

Research and Technological Guidance Division,Resources Enhancement Promotion Department, Fisheries Agency of Japan1-2-1 Kasumigaseki, Chiyoda-ku, Tokyo 100-8907 TEL: 03-6744-2030

Central Laboratory, Marine Ecology Research Institute300 Iwawada, Onjuku-machi, Isumi-gun, Chiba 299-5105 TEL: 0470-68-5111

This pamphlet is prepared as part of the promotion project for the monitoring survey of the effect of radioactive materials in FY2019.

Results of the inspection of radioactive materials in �shery products are available on the website of the Fisheries Agency. Pamphlets discussing various questions concerning radioactive materials in �sh from a scienti�c perspective are also available on the website of the Japan Fisheries Research and Education Agency.

We can get

more detailed information

from the websites

and pamphlets.

Fisheries Agency Radioactive Materials Search

Website of the Japan Fisheries Research and Education Agency:

FAQ for Radioactivity and Fish (in Japanese)

http://www.fra.affrc.go.jp/bulletin/radioactivity_pamphlet2018/cover_index.html

Page 2: Summary for understanding

Let's learn about �sheriesin Fukushima!Preface

The accident at the Tokyo Electric Power Company's Fukushima Daiichi Nuclear Power Station in March 2011 resulted in the leakage of radioactive materials and led to concerns over the contamination of �shery products.

To ensure food safety, the standard limits for radioactive materials in food are established and relevant prefectures conduct the monitoring inspections based on the guideline, "Concepts of Inspection Planning and the Establishment and Cancellation of Items and Areas to which Restriction on Distribution and/or Consumption of Foods concerned Applies" (revised on March 23, 2020) developed by the Nuclear Emergency Response Headquarters (whose director-general is the Prime Minister).

The Fisheries Agency is systematically conducting monitoring surveys for radioactive materials for marine and freshwater �shery products in East Japan to ensure the safety of �shery products and to promptly provide correct information concerning radioactive materials in such products.

Preface/Table of Contents .............................................................. 1

Let's learn about �sheries in Fukushima........................................ 2

Structure of the monitoring inspection for radioactive materials in food .... 3

Framework of the monitoring inspections...................................... 3

Process of the actual inspection ................................................... 4

Finding from the results of the monitoring inspections

Concentration of radioactive cesium in marine �sh species

Results of the analysis of radioactive cesium in marine �sh species ......... 5

Excess ratio for the standard limit (marine �sh species).......................... 6

Changes in radioactive cesium concentration in major marine �sh species ... 6

Concentration of radioactive cesium in freshwater �sh species

Results of the analysis of radioactive cesium in freshwater �sh species.... 7

Excess ratio for the standard limit (freshwater �sh species) .................... 8

Changes in radioactive cesium concentration in major freshwater �sh species ... 8

Column............................................................................................. 9

Table ofContents

Trial �shing operations and sales of catches with a lower radioactive level have been conducted since June 2012 to examine evaluations at shipped markets and gain basic information needed to resume �shery operations in Fukushima prefecture.

Meetings are held to

discuss which �sh species

are to be captured.

Fishermen catch

�sh determined in

the meeting.

All �sh are to be

shipped only after their

safety is con�rmed.

Fish ensured to

be safe are sold

in the market.

Samples extracted from the

catch are tested for radioactive

materials to ensure safety.

Target species of the trial �shing operation: All marine �sh speciesNote 1: The �sheries products for shipping are limited to those that are below 50

Bq/kg for radioactive cesium level (the voluntary limit of Fukushima Prefectural Federation of Fisheries Co-operative Associations) (cf. the standard limit of the Japanese government: 100 Bq/kg)

Note 2: As of March 1, 2020, there are no �sh species subject to restrictions on distribution issued by the Director-General of the Nuclear Emergency Response Headquarters

Landing Olive �ounder landed Fish auction

Shipped �sh are con�rmed to be safe.

To the dining table

It has been nine years since the accident, and safety

has been con�rmed in all marine �sh species.

1 2

Page 3: Summary for understanding

Let's learn about �sheriesin Fukushima!Preface

The accident at the Tokyo Electric Power Company's Fukushima Daiichi Nuclear Power Station in March 2011 resulted in the leakage of radioactive materials and led to concerns over the contamination of �shery products.

To ensure food safety, the standard limits for radioactive materials in food are established and relevant prefectures conduct the monitoring inspections based on the guideline, "Concepts of Inspection Planning and the Establishment and Cancellation of Items and Areas to which Restriction on Distribution and/or Consumption of Foods concerned Applies" (revised on March 23, 2020) developed by the Nuclear Emergency Response Headquarters (whose director-general is the Prime Minister).

The Fisheries Agency is systematically conducting monitoring surveys for radioactive materials for marine and freshwater �shery products in East Japan to ensure the safety of �shery products and to promptly provide correct information concerning radioactive materials in such products.

Preface/Table of Contents .............................................................. 1

Let's learn about �sheries in Fukushima........................................ 2

Structure of the monitoring inspection for radioactive materials in food .... 3

Framework of the monitoring inspections...................................... 3

Process of the actual inspection ................................................... 4

Finding from the results of the monitoring inspections

Concentration of radioactive cesium in marine �sh species

Results of the analysis of radioactive cesium in marine �sh species ......... 5

Excess ratio for the standard limit (marine �sh species).......................... 6

Changes in radioactive cesium concentration in major marine �sh species ... 6

Concentration of radioactive cesium in freshwater �sh species

Results of the analysis of radioactive cesium in freshwater �sh species.... 7

Excess ratio for the standard limit (freshwater �sh species) .................... 8

Changes in radioactive cesium concentration in major freshwater �sh species ... 8

Column............................................................................................. 9

Table ofContents

Trial �shing operations and sales of catches with a lower radioactive level have been conducted since June 2012 to examine evaluations at shipped markets and gain basic information needed to resume �shery operations in Fukushima prefecture.

Meetings are held to

discuss which �sh species

are to be captured.

Fishermen catch

�sh determined in

the meeting.

All �sh are to be

shipped only after their

safety is con�rmed.

Fish ensured to

be safe are sold

in the market.

Samples extracted from the

catch are tested for radioactive

materials to ensure safety.

Target species of the trial �shing operation: All marine �sh speciesNote 1: The �sheries products for shipping are limited to those that are below 50

Bq/kg for radioactive cesium level (the voluntary limit of Fukushima Prefectural Federation of Fisheries Co-operative Associations) (cf. the standard limit of the Japanese government: 100 Bq/kg)

Note 2: As of March 1, 2020, there are no �sh species subject to restrictions on distribution issued by the Director-General of the Nuclear Emergency Response Headquarters

Landing Olive �ounder landed Fish auction

Shipped �sh are con�rmed to be safe.

To the dining table

It has been nine years since the accident, and safety

has been con�rmed in all marine �sh species.

1 2

Page 4: Summary for understanding

1

2

3

100 Bq/kgor less

Structure of the monitoring inspectionfor radioactive materials in food

Process of the actualinspection

What does the standard limit mean?What does the standard limit mean?

In Japan, the standard limit for radioactive materials in general foods is set at 100 Bq/kg. This is lower than the strictest value (120 Bq/kg) of all thresholds for all age groups, which are set by taking into account differences in preferences and amount of food consumption among different age groups and sexes. The level of the standard limit ensures that the lifetime effect of radioactive materials in food is suf�ciently low as to be safe even when a person continues to eat the food (1 milli-sievert or less per year). This standard limit is safe for all age groups including infants.

Source: Compiled based on The Story of Food and Radioactive Materials (Ministry of Health, Labour and Welfare and others)

Monitoring areas

Target species

Frequency

Monitoring plan is developed mainly by local governments

Framework of the monitoring inspections

Shipping

・If the radioactive cesium level is higher than the standard limit at a single location, the relevant local government requests producers to suspend shipping voluntarily.

・If the radioactive cesium level is higher than the standard limit at multiple locations, the national government instructs restriction on distribution.

Request for voluntary suspension orinstruction of restriction on distribution

If the radioactivity level exceeds the standard limit?A voluntary suspension or restriction on distribution will be implemented regarding distribution of the relevant �sh species.

Fishery products exceeding the standard limit would not be distributed to the market.

Measurement of body length and weight

Place into an analytical beaker

AnalysisThe concentration of radioactive materials per kilogram (Bq/kg) for the edible portion is obtained as the result of the measurement.

Preparation of minceEdible parts of the �sh (mainly muscle) are thoroughly minced for the test.

Safety iscon�rmed by

the inspections.

ShippingTo thediningtable

This is howthe radioactive materials

is detected.

106

103

10 500 1000 1500

Energy (keV)

Receipt of �shery productsFishery products sent from local ports are received, and checked for catch location and species.

4

5

An example of ameasurement result

Discussion on left items and development of plans.

Implemen-tation of

the monitoring

survey

Am

ount

of d

etec

ted

rad

iatio

n

Fishery products are

inspected following

the appropriate process.

Result exceeded the standard limit

(100 Bq/kg)

3 4

Page 5: Summary for understanding

1

2

3

100 Bq/kgor less

Structure of the monitoring inspectionfor radioactive materials in food

Process of the actualinspection

What does the standard limit mean?What does the standard limit mean?

In Japan, the standard limit for radioactive materials in general foods is set at 100 Bq/kg. This is lower than the strictest value (120 Bq/kg) of all thresholds for all age groups, which are set by taking into account differences in preferences and amount of food consumption among different age groups and sexes. The level of the standard limit ensures that the lifetime effect of radioactive materials in food is suf�ciently low as to be safe even when a person continues to eat the food (1 milli-sievert or less per year). This standard limit is safe for all age groups including infants.

Source: Compiled based on The Story of Food and Radioactive Materials (Ministry of Health, Labour and Welfare and others)

Monitoring areas

Target species

Frequency

Monitoring plan is developed mainly by local governments

Framework of the monitoring inspections

Shipping

・If the radioactive cesium level is higher than the standard limit at a single location, the relevant local government requests producers to suspend shipping voluntarily.

・If the radioactive cesium level is higher than the standard limit at multiple locations, the national government instructs restriction on distribution.

Request for voluntary suspension orinstruction of restriction on distribution

If the radioactivity level exceeds the standard limit?A voluntary suspension or restriction on distribution will be implemented regarding distribution of the relevant �sh species.

Fishery products exceeding the standard limit would not be distributed to the market.

Measurement of body length and weight

Place into an analytical beaker

AnalysisThe concentration of radioactive materials per kilogram (Bq/kg) for the edible portion is obtained as the result of the measurement.

Preparation of minceEdible parts of the �sh (mainly muscle) are thoroughly minced for the test.

Safety iscon�rmed by

the inspections.

ShippingTo thediningtable

This is howthe radioactive materials

is detected.

106

103

10 500 1000 1500

Energy (keV)

Receipt of �shery productsFishery products sent from local ports are received, and checked for catch location and species.

4

5

An example of ameasurement result

Discussion on left items and development of plans.

Implemen-tation of

the monitoring

survey

Am

ount

of d

etec

ted

rad

iatio

n

Fishery products are

inspected following

the appropriate process.

Result exceeded the standard limit

(100 Bq/kg)

3 4

Page 6: Summary for understanding

Concentration of radioactive cesiumin marine �sh species Excess ratio for the standard limit

Results of the analysis of radioactive cesium in marine �sh speciesImmediately after the nuclear power station accident, about 30% of samples in Fukushima prefecture exceeded the current standard limit (100 Bq/kg). Since then, the number of samples exceeding the standard limit tends to decrease with the passage of time. In Fukushima prefecture, no sample has exceeded the standard limit since February 2019, and in prefectures other than Fukushima, no sample has exceeded the standard limit since September 2014.

Changes in radioactive cesium concentration in major marine �sh speciesSome samples of surface-layer �sh (e.g. juvenile Japanese sandlance and whitebait) and demersal �sh (e.g. olive founder) exceeded the current standard limit (100 Bq/kg) immediately after the nuclear power station accident, but the number of such samples and the concentration of radioactive cesium detected has promptly decreased with the passage of time. Currently, radioactive cesium levels are signi�cantly below the standard limit for samples.

Marine �sh species

10

100

1,000

10,000

100,000

134 C

s+13

7 Cs

(Bq/

kg)

250

200

150

100

50

134 C

s+13

7 Cs

(Bq/

kg)

2017 2018

10

100

1,000

10,000

100,000

2019

Surface-layer �sh(juvenile Japanese sandlance and whitebait) Demersal �sh (olive founder)

Below the detection limit

← Detailed information is available in the column on the last page.

Below thedetection limit

Below thedetection limit

Other prefectures

Fukushima prefecture exceeding 100 Bq/kg

below 100 Bq/kg

(FY)(FY)

Olive �ounderJuvenile Japanese sandlance

Whitebait

As of January 31, 2020

2011

2012

2013

2014

2015

2016

2018

2019

2017

2011

2012

2013

2014

2015

2016

2017

2018

2019

Below thedetection limit

10,000

(Samples)

8,000

6,000

4,000

2,000

020182011 2012 2013 2014 2015 2016

1,077

791

18148 0 0

1

1,997

5,4797,666

8,705 8,633 8,842

6,229

0

4,676

2017

0

8,559

2011 2012 2013 2014 2015 2016

10,000

(Samples)

8,000

6,000

4,000

2,000

02017

112

51 122

00

0

4,249

9,866 9,528 8,9927,745 7,086 6,317

0

4,417

2018

0

5,579

2019(FY)

2019(FY)

0

5

10

15

20

25

30

20182017201620152014201320122011

(%)

Exce

ss ra

tio fo

r the

lim

it (1

00 B

q/kg

)

0%0% 0% 0.01% 0%

2019(FY)

Total number of samples: 126,840

Number of samples exceeding 100 Bq/kg: 2,275

Number of samples below 100 Bq/kg: 124,565

Since FY2015, only one sample (detected in FY2018) has exceeded the standard limit.

(As of January 31, 2020)

5 6

Page 7: Summary for understanding

Concentration of radioactive cesiumin marine �sh species Excess ratio for the standard limit

Results of the analysis of radioactive cesium in marine �sh speciesImmediately after the nuclear power station accident, about 30% of samples in Fukushima prefecture exceeded the current standard limit (100 Bq/kg). Since then, the number of samples exceeding the standard limit tends to decrease with the passage of time. In Fukushima prefecture, no sample has exceeded the standard limit since February 2019, and in prefectures other than Fukushima, no sample has exceeded the standard limit since September 2014.

Changes in radioactive cesium concentration in major marine �sh speciesSome samples of surface-layer �sh (e.g. juvenile Japanese sandlance and whitebait) and demersal �sh (e.g. olive founder) exceeded the current standard limit (100 Bq/kg) immediately after the nuclear power station accident, but the number of such samples and the concentration of radioactive cesium detected has promptly decreased with the passage of time. Currently, radioactive cesium levels are signi�cantly below the standard limit for samples.

Marine �sh species

10

100

1,000

10,000

100,000

134 C

s+13

7 Cs

(Bq/

kg)

250

200

150

100

50

134 C

s+13

7 Cs

(Bq/

kg)

2017 2018

10

100

1,000

10,000

100,000

2019

Surface-layer �sh(juvenile Japanese sandlance and whitebait) Demersal �sh (olive founder)

Below the detection limit

← Detailed information is available in the column on the last page.

Below thedetection limit

Below thedetection limit

Other prefectures

Fukushima prefecture exceeding 100 Bq/kg

below 100 Bq/kg

(FY)(FY)

Olive �ounderJuvenile Japanese sandlance

Whitebait

As of January 31, 2020

2011

2012

2013

2014

2015

2016

2018

2019

2017

2011

2012

2013

2014

2015

2016

2017

2018

2019

Below thedetection limit

10,000

(Samples)

8,000

6,000

4,000

2,000

020182011 2012 2013 2014 2015 2016

1,077

791

18148 0 0

1

1,997

5,4797,666

8,705 8,633 8,842

6,229

0

4,676

2017

0

8,559

2011 2012 2013 2014 2015 2016

10,000

(Samples)

8,000

6,000

4,000

2,000

02017

112

51 122

00

0

4,249

9,866 9,528 8,9927,745 7,086 6,317

0

4,417

2018

0

5,579

2019(FY)

2019(FY)

0

5

10

15

20

25

30

20182017201620152014201320122011

(%)

Exce

ss ra

tio fo

r the

lim

it (1

00 B

q/kg

)

0%0% 0% 0.01% 0%

2019(FY)

Total number of samples: 126,840

Number of samples exceeding 100 Bq/kg: 2,275

Number of samples below 100 Bq/kg: 124,565

Since FY2015, only one sample (detected in FY2018) has exceeded the standard limit.

(As of January 31, 2020)

5 6

Page 8: Summary for understanding

Concentration of radioactive cesiumin freshwater �sh species Excess ratio for the standard limit

Results of the analysis of radioactive cesium in freshwater �sh speciesImmediately after the nuclear power station accident, many freshwater �sh species exceeded the current standard limit (100 Bq/kg). Since then, the number of samples exceeding the standard limit tends to decrease with the passage of time.

Changes in radioactive cesium concentration in major freshwater �sh speciesThe number of samples of wild IWANA (char) and YAMAME (land-locked cherry salmon) exceeding the standard limit is substantially decreased compared to immediately after the accident. At the same time, no samples of cultured IWANA and YAMAME have exceeded the standard limit.

Example of freshwater �sh species(cultured IWANA and YAMAME)

Example of freshwater �sh species(wild IWANA and YAMAME)

134 C

s+13

7 Cs

(Bq/

kg)

10

100

(FY)

Below the detection limit

Other prefectures

Fukushima prefecture

←Detailed information is available in the column on the last page.

exceeding 100 Bq/kg

below 100 Bq/kg

Freshwater �sh species

IWANA (wild)YAMAME (wild)

IWANA (cultured)YAMAME (cultured)

The number of samples

exceeding the limit is

gradually decreasing.

As of January 31, 2020

2011

2012

2013

2014

2015

2016

2017

2018

2019

2011

2012

2013

2014

2015

2016

2017

2018

2019

134 C

s+13

7 Cs

(Bq/

kg)

100,000

10

100

1,000

10,000

2017 2018 2019

100

400

500

300

200

(FY)

Below thedetection limit

Below thedetection limit

Below thedetection limit

2011 2012 2013 2014 2015 2016 2017

1,200

(Samples)

800

600

400

200

1,000

0

17388

27

74 8

372

567

911

628697

742

4

1,107

2018

5

904

57

626

20182011 2012 2013 2014 2015 2016 2017

3,000

2,500

2,000

1,500

1,000

500

0

114

163 52

23

7

73

482

2,560 2,573

2,2141,781

1,5301,300

2

817

0

1,204

2019(FY)

2019(FY)

(Samples)

0

5

10

15

20

25

30

20182017201620152014201320122011

0.6% 0.5% 0.5% 0.2% 0.3%

(%)

2019(FY)

Exce

ss ra

tio fo

r the

lim

it (1

00 B

q/kg

)

Total number of samples: 21,759

Number of samples exceeding 100 Bq/kg: 744

Number of samples below 100 Bq/kg: 21,015

Some �sh species exceed the standard limit. However, the frequency of such samples and the concentration of radioactive cesium detected tend to decrease year by year.

As of January 31, 2020

7 8

Page 9: Summary for understanding

Concentration of radioactive cesiumin freshwater �sh species Excess ratio for the standard limit

Results of the analysis of radioactive cesium in freshwater �sh speciesImmediately after the nuclear power station accident, many freshwater �sh species exceeded the current standard limit (100 Bq/kg). Since then, the number of samples exceeding the standard limit tends to decrease with the passage of time.

Changes in radioactive cesium concentration in major freshwater �sh speciesThe number of samples of wild IWANA (char) and YAMAME (land-locked cherry salmon) exceeding the standard limit is substantially decreased compared to immediately after the accident. At the same time, no samples of cultured IWANA and YAMAME have exceeded the standard limit.

Example of freshwater �sh species(cultured IWANA and YAMAME)

Example of freshwater �sh species(wild IWANA and YAMAME)

134 C

s+13

7 Cs

(Bq/

kg)

10

100

(FY)

Below the detection limit

Other prefectures

Fukushima prefecture

←Detailed information is available in the column on the last page.

exceeding 100 Bq/kg

below 100 Bq/kg

Freshwater �sh species

IWANA (wild)YAMAME (wild)

IWANA (cultured)YAMAME (cultured)

The number of samples

exceeding the limit is

gradually decreasing.

As of January 31, 2020

2011

2012

2013

2014

2015

2016

2017

2018

2019

2011

2012

2013

2014

2015

2016

2017

2018

2019

134 C

s+13

7 Cs

(Bq/

kg)

100,000

10

100

1,000

10,000

2017 2018 2019

100

400

500

300

200

(FY)

Below thedetection limit

Below thedetection limit

Below thedetection limit

2011 2012 2013 2014 2015 2016 2017

1,200

(Samples)

800

600

400

200

1,000

0

17388

27

74 8

372

567

911

628697

742

4

1,107

2018

5

904

57

626

20182011 2012 2013 2014 2015 2016 2017

3,000

2,500

2,000

1,500

1,000

500

0

114

163 52

23

7

73

482

2,560 2,573

2,2141,781

1,5301,300

2

817

0

1,204

2019(FY)

2019(FY)

(Samples)

0

5

10

15

20

25

30

20182017201620152014201320122011

0.6% 0.5% 0.5% 0.2% 0.3%

(%)

2019(FY)

Exce

ss ra

tio fo

r the

lim

it (1

00 B

q/kg

)

Total number of samples: 21,759

Number of samples exceeding 100 Bq/kg: 744

Number of samples below 100 Bq/kg: 21,015

Some �sh species exceed the standard limit. However, the frequency of such samples and the concentration of radioactive cesium detected tend to decrease year by year.

As of January 31, 2020

7 8

Page 10: Summary for understanding

Cooperation with the International Atomic Energy Agency (IAEA)

Column

The IAEA and Japanese laboratories measured radioactive materials using the same specimens extracted from �shery products and the measurement ability of the Japanese laboratories was examined (i.e. pro�ciency test). As a result, the methodology for radioactive material measurement practiced by Japanese laboratories were con�rmed to be appropriate and have a high level of accuracy and competency.

What is the detection limit?Column

The detection limit means the lowest concentration of target material that an analytical device can detect. The value becomes lower as the sample weight and/or duration of measurement increase, meaning detection and measurement of much lower concentrations becomes possible. On the other hand, this also means the number of samples to be analyzed becomes less. Therefore, a required detection limit is maintained for the speci�c purpose of analysis, and the value of the detection limit is presented to clarify that the outcome of the inspection is suf�ciently reliable.

Source: Compiled based on “Analysis of radioactive materials” (in Japanese) (Ministry of Agriculture, Forestry and Fisheries)

Change in radioactive cesium concentrationin marine �shery products before the nuclearpower plant accident

Column

The concentration of radioactive cesium (137Cs) in marine �shery products such as �sh and octopus had remained below 1 Bq/kg from 1983 to 2010. Radioactive cesium was present in the environment previously due to the effect of atmospheric nuclear explosion tests conducted mainly in the northern hemisphere.

3

2

1

Year of sampling

Bq/kg (fresh �shery products)

Detectionlimit

Con

cent

ratio

n

Cesium-137

Chronological change of radioactive cesium (137Cs)in marine �shery products

The graph above indicates the radioactive cesium levels measured in the waters around nuclear power stations in Japan.For details, please refer to “Protection of Fishing Grounds” (in Japanese) on the website of the Marine Ecology Research Institute. (URL: https://www.kaiseiken.or.jp/publish/itaku/itakuseika.html)

Why is the detection limit different depending on the sample?Q

ADifferences in detection limits occur when performing analyses even using the same device if the weight of the sample placed into the beaker and/or the duration of the measurement are different. The inspection of radioactive materials in food is implemented in accordance with the of�cial testing method, “Testing Methods for Radioactive Substances in Food” and

“Application of testing methods for radioactive substances in food” provided by the Ministry of Health, Labour and Welfare. The detection limit is set to be well below the standard limit (100 Bq/kg).

No. Radioactive cesium (137Cs) [unit: Bq/kg]

9617

9618

9619

9620

Fish species

Chub mackerel

Chub mackerel

Hilgendorf saucord

Japanese sardine

Prefecture

Miyagi

Miyagi

Miyagi

Miyagi

Below the detection limit (<0.571)

Below the detection limit (<2.98)

Below the detection limit (<3.59)

Below the detection limit (<4.34)

Table: Example of the result of the inspectionof radioactive materials in �shery products

(Source) the website of the Fisheries Agency

1983198419851986198719881989199019911992199319941995199619971998199920002001200220032004200520062007200820092010

The detection limit dropswhen the weight of the

measured sample increases.

Radioactive cesiumwas present in small amounts

before the nuclear powerstation accident.

This value is thedetection limit.

9 10

Page 11: Summary for understanding

Cooperation with the International Atomic Energy Agency (IAEA)

Column

The IAEA and Japanese laboratories measured radioactive materials using the same specimens extracted from �shery products and the measurement ability of the Japanese laboratories was examined (i.e. pro�ciency test). As a result, the methodology for radioactive material measurement practiced by Japanese laboratories were con�rmed to be appropriate and have a high level of accuracy and competency.

What is the detection limit?Column

The detection limit means the lowest concentration of target material that an analytical device can detect. The value becomes lower as the sample weight and/or duration of measurement increase, meaning detection and measurement of much lower concentrations becomes possible. On the other hand, this also means the number of samples to be analyzed becomes less. Therefore, a required detection limit is maintained for the speci�c purpose of analysis, and the value of the detection limit is presented to clarify that the outcome of the inspection is suf�ciently reliable.

Source: Compiled based on “Analysis of radioactive materials” (in Japanese) (Ministry of Agriculture, Forestry and Fisheries)

Change in radioactive cesium concentrationin marine �shery products before the nuclearpower plant accident

Column

The concentration of radioactive cesium (137Cs) in marine �shery products such as �sh and octopus had remained below 1 Bq/kg from 1983 to 2010. Radioactive cesium was present in the environment previously due to the effect of atmospheric nuclear explosion tests conducted mainly in the northern hemisphere.

3

2

1

Year of sampling

Bq/kg (fresh �shery products)

Detectionlimit

Con

cent

ratio

n

Cesium-137

Chronological change of radioactive cesium (137Cs)in marine �shery products

The graph above indicates the radioactive cesium levels measured in the waters around nuclear power stations in Japan.For details, please refer to “Protection of Fishing Grounds” (in Japanese) on the website of the Marine Ecology Research Institute. (URL: https://www.kaiseiken.or.jp/publish/itaku/itakuseika.html)

Why is the detection limit different depending on the sample?Q

ADifferences in detection limits occur when performing analyses even using the same device if the weight of the sample placed into the beaker and/or the duration of the measurement are different. The inspection of radioactive materials in food is implemented in accordance with the of�cial testing method, “Testing Methods for Radioactive Substances in Food” and

“Application of testing methods for radioactive substances in food” provided by the Ministry of Health, Labour and Welfare. The detection limit is set to be well below the standard limit (100 Bq/kg).

No. Radioactive cesium (137Cs) [unit: Bq/kg]

9617

9618

9619

9620

Fish species

Chub mackerel

Chub mackerel

Hilgendorf saucord

Japanese sardine

Prefecture

Miyagi

Miyagi

Miyagi

Miyagi

Below the detection limit (<0.571)

Below the detection limit (<2.98)

Below the detection limit (<3.59)

Below the detection limit (<4.34)

Table: Example of the result of the inspectionof radioactive materials in �shery products

(Source) the website of the Fisheries Agency

1983198419851986198719881989199019911992199319941995199619971998199920002001200220032004200520062007200820092010

The detection limit dropswhen the weight of the

measured sample increases.

Radioactive cesiumwas present in small amounts

before the nuclear powerstation accident.

This value is thedetection limit.

9 10

Page 12: Summary for understanding

March 2020

Fisheries Agency of JapanFo

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consumption with peace of m

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Summary forunderstanding

the monitoring inspectionof radioactive materials

Website of the Fisheries Agency (in English): https://www.jfa.maff.go.jp/e/inspection/index.html

Research and Technological Guidance Division,Resources Enhancement Promotion Department, Fisheries Agency of Japan1-2-1 Kasumigaseki, Chiyoda-ku, Tokyo 100-8907 TEL: 03-6744-2030

Central Laboratory, Marine Ecology Research Institute300 Iwawada, Onjuku-machi, Isumi-gun, Chiba 299-5105 TEL: 0470-68-5111

This pamphlet is prepared as part of the promotion project for the monitoring survey of the effect of radioactive materials in FY2019.

Results of the inspection of radioactive materials in �shery products are available on the website of the Fisheries Agency. Pamphlets discussing various questions concerning radioactive materials in �sh from a scienti�c perspective are also available on the website of the Japan Fisheries Research and Education Agency.

We can get

more detailed information

from the websites

and pamphlets.

Fisheries Agency Radioactive Materials Search

Website of the Japan Fisheries Research and Education Agency:

FAQ for Radioactivity and Fish (in Japanese)

http://www.fra.affrc.go.jp/bulletin/radioactivity_pamphlet2018/cover_index.html