**2.1 Separation of tritium from air**

The measurement of tritium in the atmosphere is begun with air sampling where the solid absorbent such as silica gel and molecular sieve generally used to collect air sample. The silica gel is an oxide silicate having bee nest like structure, porous, and has very wide surface (Patton et al, 1995). Each gram of silica gel has great affinity toward water molecule, so it is very effective for water absorption. Generally, the silica gel contains blue cobalt salt as an indicator of water content that can exhibit color change from blue to pink after absorbing water or water vapor. The disadvantage of silica gel use in atmospheric tritium sampling is the bond of tritiated water to silica gel grain that is take place in the surface of the grain causing an easy evaporation if it is used in high temperature environment (Patton et al, 1995).

The other solid absorbent can be used for atmospheric tritium sampling is molecular sieve that made of aluminosilicate (zeolite). The aluminosilicate is a chelat compound that can absorb the chemical substances both organic and inorganic as well as water molecule to the cavity of its molecular structure (Iida et al., 1995). The cavity of molecular sieve structure have various sizes such as 3Å (MS3A), 4Å (MS4A), 5Å (MS5A) and 10Å (MS13X).

The sampling apparatus for tritiated water vapor collection is composed of a sucking pump, a quartz tube of 0.80 m length and 0.05 m diameter, and a water bubler bottle installed at the end of the circuit to confirm the air flow (Figure 1). The atmospheric air is drawn by the pump with low flow rate of about 15 L/h and flown to the tube packed with the silica gel or molecular sieve pelet. Sampling is conducted for about 15 h, the time when the 50 g packed absorbent has been saturated absorbing the tritiated water vapor.

The tritium water vapor absorbed in the solid absorbent is then recovered by developed distillation technique using an apparatus shown in Figure 2. The distillation apparatus is composed of nitrogen gas source, a tube furnace, and a condensation system. The condensation system consists of two condensation tubes that placed in a serial arrangement

The Separation of Tritium Radionuclide from

respectively.

recovered from silica gel

recovered from molecular sieve.

**2.2 Separation of tritium from water** 

Environmental Samples by Distillation Technique 271

Figure 3 and 4 show the linear relationship between the tritiated water radioactivity in the air with those recovered from the absorbent with the correlation coefficient of 0.985 and approximately 1 for silica gel and molecular sieve, respectively. The capacity of silica gel and molecular sieve in tritiated water vapor absorption has been tested gravimetrically, and the capacity of 48.6% and 43.6% were obtained for silica gel and molecular sieve,

Fig. 3. The linear relationship between the tritiated water activity in the air with those

Fig. 4. The linear relationship between the tritiated water activity in the air with those

As stated in previous section, the tritium measurement using LSC method needs clear and colurless liquid, hence the environmental water sample with low organic matter can

Fig. 1. The apparatus for tritiated water vapor sampling

in an ice box. The quartz tube with the tritiated water vapor saturated absorbent is inserted into the tube furnace, and connected to nitrogen gas source using teflon pipe, while the other side is connected to the condensation system. The solid absorbent is heated at 400 oC under nitrogen gas flow until stable mass of solid absorbent is gained. For 50 g of absorbent about 24 h heating is needed. The vapor released from the absorbent is flowed by nitrogen gas to the condensation tubes in the ice box and condensed to liquid form that trapped in the bottom of the tubes. The trapped water is then ready to be measured using liquid scintillation counting method, such as described in section 1.2.2.

The whole system, both tritiated water vapor sampling and separation method have been tested by introducing the various activities of tritiated water vapor to the air sampling apparatus for 15 h. The absorbed tritium in the solid absorbent is then recovered using the distillation apparatus in Figure 2. The measurement of the recovered tritiated water indicates the linearity correlation between the tritiated water vapor radioactivities with those in the recovered water.

Fig. 2. Distillation apparatus to separate tritiated water vapor from the absorbent bulk.

glass wool

in an ice box. The quartz tube with the tritiated water vapor saturated absorbent is inserted into the tube furnace, and connected to nitrogen gas source using teflon pipe, while the other side is connected to the condensation system. The solid absorbent is heated at 400 oC under nitrogen gas flow until stable mass of solid absorbent is gained. For 50 g of absorbent about 24 h heating is needed. The vapor released from the absorbent is flowed by nitrogen gas to the condensation tubes in the ice box and condensed to liquid form that trapped in the bottom of the tubes. The trapped water is then ready to be measured using liquid

The whole system, both tritiated water vapor sampling and separation method have been tested by introducing the various activities of tritiated water vapor to the air sampling apparatus for 15 h. The absorbed tritium in the solid absorbent is then recovered using the distillation apparatus in Figure 2. The measurement of the recovered tritiated water indicates the linearity correlation between the tritiated water vapor radioactivities with

tube furnace

Fig. 2. Distillation apparatus to separate tritiated water vapor from the absorbent bulk.

**400 C** 

condensation tube

ice

quartz tube

water bubler

outlet

nitrogen gas ( **N2** )

Fig. 1. The apparatus for tritiated water vapor sampling

inlet

air pump

silica gel or molecular sieve

scintillation counting method, such as described in section 1.2.2.

silica gel or molecular sieve

those in the recovered water.

Figure 3 and 4 show the linear relationship between the tritiated water radioactivity in the air with those recovered from the absorbent with the correlation coefficient of 0.985 and approximately 1 for silica gel and molecular sieve, respectively. The capacity of silica gel and molecular sieve in tritiated water vapor absorption has been tested gravimetrically, and the capacity of 48.6% and 43.6% were obtained for silica gel and molecular sieve, respectively.

Fig. 3. The linear relationship between the tritiated water activity in the air with those recovered from silica gel

Fig. 4. The linear relationship between the tritiated water activity in the air with those recovered from molecular sieve.

#### **2.2 Separation of tritium from water**

As stated in previous section, the tritium measurement using LSC method needs clear and colurless liquid, hence the environmental water sample with low organic matter can

The Separation of Tritium Radionuclide from

**2.3 Separation of tritium from soil** 

and colorless water can be obtained.

Fig. 6. The apparatus for soil samples preparation

sample

**2.3.2 Organically bound tritium** 

**2.3.1 Free water tritium** 

Environmental Samples by Distillation Technique 273

Tritium in the soil is present as both free water tritium (FWT) and organically bound tritium (OBT). The soil tritium is separated from the soil bulk using modified distillation technique

The FWT sample from the soil represents tritium in the water molecule in soil particle surface and interstitial particles (Tjahaja et al., 1995). The FWT from soil sample is collected using distillation technique by heating the soil sample at 150 oC in a quartz tube and condensing the vapor released from the samples at low temperature of about 10 oC. The sample heating is conducted in a tube furnace. The distillation apparatus for soil FWT collection consists of oxygen and nitrogen gas flow system, tube furnace, and condensation system as shown in Figure 6. The condensation system consists of two condensation tubes in serial arrangement inside an ice box. A quartz tube packed with 250 g of soil samples is inserted into the furnace and connected to the gas source system in one side and to the condensation tube in another side. The soil sample is heated at 150 oC under the slow nitrogen gas flow and the vapor from the heated soil is transferred to the condensation tube to be condensed in liquid form. The distillation process of 250 g soil sample take about 30 h, nevertheless it depends on the soil water content. The FWT obtained from this process possibly contains organic material that is visually seen as unclear and yellow color liquid. In this condition, FWT distillation is necessary to remove the impurities of the FWT so clear

The dried soil sample as the residue of the FWT distillation process is combusted in the same quartz tube by increasing the temperature of the furnace to 450 oC and applying the oxygen gas to the tube to obtain OBT as liquid form. The combustion results (H2O and CO2) is flowed to the condensation tubes where the H2O gas will be condensed as liquid while the

condensation tube

nitrogen gas ( N2 ) ice

tube furnace

quartz tube

oxygen gas ( O**2** )

**450 C** 

to obtain tritium samples as water to be possible for LSC measurement.

directly prepared using simple water distillation. The distillation should be conducted in relatively low temperature of about 70 oC and the water have to be completely distilled to near dryness. The complete distillation is neccessary as tritium which has relatively higher atomic mass compared to its isotopes (hydrogen and deuterium) will be distributed in the bottom of the distillation flask and evaporated later. For the environmental water samples with high organic matter content, the distillation should be done with the addition of KMnO4 and activated carbon to decompose and absorb the organic impurities. The organic matter content in the water samples can be determined visually or using UV vis spectrophotometery method. The complete distillation is carried out at 70oC temperature.

The apparatus for environmental water sample distillation is shown in Figure 5. The apparatus is composed of round bottom flask for water samples, a glass water circulation condensor, a glass vessel with a valve in its end opening for collecting distillate, an adapter between the sample flask and the condensor that equipped with a thermometer. In the top end of the condensor vessel a glass vessel filled with silica gel absorbent is installed to avoid the laboratory atmospheric water vapour contaminates the distillate obtained. The sample heating is conducted using a mantle heater.

In order to obtain the clear and colourless ditillate, the distillation can be done once, but if the water samples contain high organic matter the distillation is conducted more than once until the clear and colurless distillate is gained.

Fig. 5. The distillation apparatus for environmental water samples preparation

### **2.3 Separation of tritium from soil**

Tritium in the soil is present as both free water tritium (FWT) and organically bound tritium (OBT). The soil tritium is separated from the soil bulk using modified distillation technique to obtain tritium samples as water to be possible for LSC measurement.

### **2.3.1 Free water tritium**

272 Distillation – Advances from Modeling to Applications

directly prepared using simple water distillation. The distillation should be conducted in relatively low temperature of about 70 oC and the water have to be completely distilled to near dryness. The complete distillation is neccessary as tritium which has relatively higher atomic mass compared to its isotopes (hydrogen and deuterium) will be distributed in the bottom of the distillation flask and evaporated later. For the environmental water samples with high organic matter content, the distillation should be done with the addition of KMnO4 and activated carbon to decompose and absorb the organic impurities. The organic matter content in the water samples can be determined visually or using UV vis spectrophotometery method. The complete distillation is carried

The apparatus for environmental water sample distillation is shown in Figure 5. The apparatus is composed of round bottom flask for water samples, a glass water circulation condensor, a glass vessel with a valve in its end opening for collecting distillate, an adapter between the sample flask and the condensor that equipped with a thermometer. In the top end of the condensor vessel a glass vessel filled with silica gel absorbent is installed to avoid the laboratory atmospheric water vapour contaminates the distillate obtained. The sample

In order to obtain the clear and colourless ditillate, the distillation can be done once, but if the water samples contain high organic matter the distillation is conducted more than once

> water coolant outlet

thermometer

sample

Fig. 5. The distillation apparatus for environmental water samples preparation

distillate

mantle heater

out at 70oC temperature.

heating is conducted using a mantle heater.

until the clear and colurless distillate is gained.

silica gel

water coolant inlet

The FWT sample from the soil represents tritium in the water molecule in soil particle surface and interstitial particles (Tjahaja et al., 1995). The FWT from soil sample is collected using distillation technique by heating the soil sample at 150 oC in a quartz tube and condensing the vapor released from the samples at low temperature of about 10 oC. The sample heating is conducted in a tube furnace. The distillation apparatus for soil FWT collection consists of oxygen and nitrogen gas flow system, tube furnace, and condensation system as shown in Figure 6. The condensation system consists of two condensation tubes in serial arrangement inside an ice box. A quartz tube packed with 250 g of soil samples is inserted into the furnace and connected to the gas source system in one side and to the condensation tube in another side. The soil sample is heated at 150 oC under the slow nitrogen gas flow and the vapor from the heated soil is transferred to the condensation tube to be condensed in liquid form. The distillation process of 250 g soil sample take about 30 h, nevertheless it depends on the soil water content. The FWT obtained from this process possibly contains organic material that is visually seen as unclear and yellow color liquid. In this condition, FWT distillation is necessary to remove the impurities of the FWT so clear and colorless water can be obtained.

Fig. 6. The apparatus for soil samples preparation

#### **2.3.2 Organically bound tritium**

The dried soil sample as the residue of the FWT distillation process is combusted in the same quartz tube by increasing the temperature of the furnace to 450 oC and applying the oxygen gas to the tube to obtain OBT as liquid form. The combustion results (H2O and CO2) is flowed to the condensation tubes where the H2O gas will be condensed as liquid while the

The Separation of Tritium Radionuclide from

distilled and measured using LSC method.

incomplete combustion process in OBT recovery.

OBT) after sample preparation.

**2.5 Separation of tritium from human urine** 

Environmental Samples by Distillation Technique 275

colorless distillate was obtained and could be measured using LSC technique. The dried grass sample in the quartz tube was then combusted at 450 oC under oxygen gas flow using tube furnace in the same apparatus. The gas released (H2O and CO2) from the combusted grass samples was flowed to the combustion tube and condensed at ice temperature. The condensed water representing the OBT of the grass as the same as the FWT was completely

The increase of tritium activity in the grass sample is followed with the increase of the recovered FWT and OBT. The correlation of tritium radioactivity in the grass with those measured after sample preparation shows linear correlation with the coefficient of 0.98, such as shown in Figure 8. A good performance of this apparatus system is indicated with the recovery efficiency of 80% for total tritium in the grass (FWT and OBT). The performance of the separation method for plant samples relatively low compared with those for soil samples relating to the complexity of organic compound in the grass leading to the

Fig. 8. The correlation of tritium radioactivity in the grass with those measured (FWT and

The presence of tritium in the air, drinking water, foods, and other consumer products is the source of human contamination with tritium (Puhakainen et al., 2007 and Trivedi et al, 2000). The detection of tritium contamination in the human body can be carried out using urine samples measurement. Nevertheless, tritium measurement in urine has a limitation relating to the body metabolite content in the urine that signicantly affect the LSC measurement (Trivedi et al., 2000; Rusconi et al, 2006). The measurement of such urine possibly to increase counting rate of tritium in the LSC measurement because of chemical luminesence from samples impurities and from β radiation emmitted by 14C bounded in organic matter of body metabolite (Rusconi et al., 2006; Groning, 2004). Such a counting result cause over estimation of tritium concentration in the urine especially in low level tritium measurement (Groning, 2004; Momoshima et al., 1986). Therefore, urine sample

CO2 will be flushed out since its condensation point is lower than the temperature in the condensation system. The combustion is held for 30 hours until all soil samples become ash. The condensed water (OBT) contains the organic matter, especially if the combustion process is not perfect. Therefore, a distillation with KMnO4 and activated charcoal addition is necessary to obtain the clear and colorless water for the LSC measurement.

The performance of the distillation apparatus for soil trtium separation has been tested by preparing 250 g of soil samples with varied tritium concentration, i.e. 180, 270, 555, and 740 Bq. A good performance of this apparatus system is indicated by the recovery efficiency of 92 % for total tritium (FWT and OBT) in the soil. The measured tritium activity in soil samples both for FWT and OBT linearly increased with the amount of given tritium activity in the soil. The correlation of tritium activities in the soil with those measured after sample preparation shows linear correlation with the coefficient of 0.99, such as shown in Figure 7.

The distillation of FWT and OBT after the heating and combustion process is necessary to be conducted to obtain the suitable sample for LSC measurement. The distillation of FWT and OBT water after the sample heating or combustion can increase the tritium analysis efficiency of about 10%.

Fig. 7. The correlation of tritium radioactivity in the soil with those measured (FWT and OBT) after sample preparation.

#### **2.4 Separation of tritium from plant**

As the same as with the soil, the tritium radionuclide in plant occur in the form of free water tritium and organically bound tritium (Konig, 1990), hence the sample preparation for tritium measurement using LSC method is the same as with those for soil sample.

The performance of the apparatus for tritium separation from plant has been tested (Tjahaja et al., 2005) using varied tritium concentration in the grass of 225, 450, 670, and 960 Bq in 230 g of fresh grass. The tritium contaminated fresh grass was packed in a quartz tube and heated at 150 oC for 30 h using tube furnace that was arranged as in Figure 6. The vapor released was condensed in condensation tube cooled by ice cube. The recovered vapor as FWT was completely distilled by KMnO4 and activated charcoal addition until clear and

CO2 will be flushed out since its condensation point is lower than the temperature in the condensation system. The combustion is held for 30 hours until all soil samples become ash. The condensed water (OBT) contains the organic matter, especially if the combustion process is not perfect. Therefore, a distillation with KMnO4 and activated charcoal addition

The performance of the distillation apparatus for soil trtium separation has been tested by preparing 250 g of soil samples with varied tritium concentration, i.e. 180, 270, 555, and 740 Bq. A good performance of this apparatus system is indicated by the recovery efficiency of 92 % for total tritium (FWT and OBT) in the soil. The measured tritium activity in soil samples both for FWT and OBT linearly increased with the amount of given tritium activity in the soil. The correlation of tritium activities in the soil with those measured after sample preparation shows linear correlation with the coefficient of 0.99,

The distillation of FWT and OBT after the heating and combustion process is necessary to be conducted to obtain the suitable sample for LSC measurement. The distillation of FWT and OBT water after the sample heating or combustion can increase the tritium analysis

Fig. 7. The correlation of tritium radioactivity in the soil with those measured (FWT and

As the same as with the soil, the tritium radionuclide in plant occur in the form of free water tritium and organically bound tritium (Konig, 1990), hence the sample preparation for

The performance of the apparatus for tritium separation from plant has been tested (Tjahaja et al., 2005) using varied tritium concentration in the grass of 225, 450, 670, and 960 Bq in 230 g of fresh grass. The tritium contaminated fresh grass was packed in a quartz tube and heated at 150 oC for 30 h using tube furnace that was arranged as in Figure 6. The vapor released was condensed in condensation tube cooled by ice cube. The recovered vapor as FWT was completely distilled by KMnO4 and activated charcoal addition until clear and

tritium measurement using LSC method is the same as with those for soil sample.

is necessary to obtain the clear and colorless water for the LSC measurement.

such as shown in Figure 7.

efficiency of about 10%.

OBT) after sample preparation.

**2.4 Separation of tritium from plant** 

colorless distillate was obtained and could be measured using LSC technique. The dried grass sample in the quartz tube was then combusted at 450 oC under oxygen gas flow using tube furnace in the same apparatus. The gas released (H2O and CO2) from the combusted grass samples was flowed to the combustion tube and condensed at ice temperature. The condensed water representing the OBT of the grass as the same as the FWT was completely distilled and measured using LSC method.

The increase of tritium activity in the grass sample is followed with the increase of the recovered FWT and OBT. The correlation of tritium radioactivity in the grass with those measured after sample preparation shows linear correlation with the coefficient of 0.98, such as shown in Figure 8. A good performance of this apparatus system is indicated with the recovery efficiency of 80% for total tritium in the grass (FWT and OBT). The performance of the separation method for plant samples relatively low compared with those for soil samples relating to the complexity of organic compound in the grass leading to the incomplete combustion process in OBT recovery.

Fig. 8. The correlation of tritium radioactivity in the grass with those measured (FWT and OBT) after sample preparation.

#### **2.5 Separation of tritium from human urine**

The presence of tritium in the air, drinking water, foods, and other consumer products is the source of human contamination with tritium (Puhakainen et al., 2007 and Trivedi et al, 2000). The detection of tritium contamination in the human body can be carried out using urine samples measurement. Nevertheless, tritium measurement in urine has a limitation relating to the body metabolite content in the urine that signicantly affect the LSC measurement (Trivedi et al., 2000; Rusconi et al, 2006). The measurement of such urine possibly to increase counting rate of tritium in the LSC measurement because of chemical luminesence from samples impurities and from β radiation emmitted by 14C bounded in organic matter of body metabolite (Rusconi et al., 2006; Groning, 2004). Such a counting result cause over estimation of tritium concentration in the urine especially in low level tritium measurement (Groning, 2004; Momoshima et al., 1986). Therefore, urine sample

The Separation of Tritium Radionuclide from

Fig. 10. The scheme of urine sample preparation by B method

Fig. 11. The scheme of urine sample preparation by C method

Environmental Samples by Distillation Technique 277

+ 2.5 g active carbon Complete distillation at 70 <sup>o</sup>

**C method D method** 2 mL urine

Urine distillate (from B method)

Urine distillate

2 mL urine distillate

2 mL urine + 13 mL scintillator

LSC measurement (1 h)

for 1 d

+ 13 mL scintillator, mixed, stored in the dark and cool for 1 d C

2 mL urine + 13 mL scintillator

LSC measurement (1 h)

+ 3 g KMnO4 +0.25 mL H2SO4 Complete distillation at 70 <sup>o</sup>

+ 13 mL scintillator, mixed, stored in the dark and cool

C

Clear urine (from A method)

Urine distillate

preparation is important to be applied before LSC measurement to reduce body metabolite content affecting the measurement result.

Several urine sample preparation methods have been performance tested for low level tritium (Tjahaja, 2009). Six methods, named A, B, C, D, E, and F, were applied to two urine samples already contaminated with tritium in the concentration of 0.5 Bq/mL and 1 Bq/mL. The method efficiency was analyzed based on the tritium activity recovered in the urine sample after the preparation.

In A - E method, sample preparations were applied such as described in the scheme in the Figure 9-13 (Momoshima et al, 1986; Bhatt et al., 2002), while in the F method an amount of urine sample was directly measured using LSC.

Fig. 9. The scheme of urine sample preparation by A method

preparation is important to be applied before LSC measurement to reduce body metabolite

Several urine sample preparation methods have been performance tested for low level tritium (Tjahaja, 2009). Six methods, named A, B, C, D, E, and F, were applied to two urine samples already contaminated with tritium in the concentration of 0.5 Bq/mL and 1 Bq/mL. The method efficiency was analyzed based on the tritium activity recovered in the

In A - E method, sample preparations were applied such as described in the scheme in the Figure 9-13 (Momoshima et al, 1986; Bhatt et al., 2002), while in the F method an amount of

> + 13 mL scintillator, mixed, stored in the dark and cool

for 1 d

2 mL urine

2 mL urine + 13 mL scintillator

LSC measurement (1 h)

+ 2.5 g active carbon

+ HTO, mixed

content affecting the measurement result.

urine sample was directly measured using LSC.

Fig. 9. The scheme of urine sample preparation by A method

urine sample + HTO

50 mL urine sample

clear urine

urine sample + active carbon

**B method** 

filtered

urine sample after the preparation.

Fig. 10. The scheme of urine sample preparation by B method

Fig. 11. The scheme of urine sample preparation by C method

The Separation of Tritium Radionuclide from

shown in Figure 5 in section 2.2.

flushed out by nitogen gas flow for about 10 minutes.

the F method, numbers 2-6 represent the A – E method.

Environmental Samples by Distillation Technique 279

The performance test result can be seen in Figure 14 and 15 for tritium concentration in the urine of 0.5 Bq/mL and 1 Bq/mL, respectively. They indicate that the E method has the highest eficiency with the average of 35% and 58% for tritium concentration of 0.5 Bq/mL and 1 Bq/ mL. In the F method that is direct LSC measurement, the tritium activity is not detected in the recovered urine as the same as with those for A and B method. The separation procedure shown in Figure 10-13 is carried out using distillation apparatus

For tritium measurement in the urine the E method is used. The 24 h urine sample is collected in a plastic bottle, and about 25 mL of the sample is added with 1.25 mg of active charcoal, shaked vigorously for about 30 minutes, then filtered using filter paper to obtain clear and colorless filtrate that free of particulate matter. The filtrate is then again added with active charccoal and distilled completely at 70 oC to eliminate the yellow color of the first filtrate that can alter measurement using LSC device (Puhakainen et al., 2007; Momoshima et al, 1986). The distilate obtained is then added with 1.5 g KMnO4 and 0.05 g NaOH to destruct the urine organic compound, and again distilled completely at 70 oC. The distillate is then added with 0.125 mL concentrate sulfuric acid to destruct carbonate compound resulted from previous reaction. The CO2 released from the reaction is then

Fig. 14. The method efficiency of 0.5 Bq/mL urine sample preparation. Number 1 represents

Fig. 12. The scheme of urine sample preparation by D method

Fig. 13. The scheme of urine sample preparation by E method

+ 3 g KMnO4 +0.1g NaOH Complete distillation at 70 <sup>o</sup>

+ 13 mL scintillator, mixed, stored in the dark and cool for 1 d

Clear and colorless urine

2 mL clear and colorless urine

2 mL urine + 13 mL scintillator

LSC measurement (1 h)

for 1 d

+ N2

Urine distillate (from D method)

Urine distillate (from B method)

**E method** 

Urine distillate

LSC measurement (1 h)

+ 0.25 mL concentrate H2SO4

+ 13 mL scintillator, mixed, stored in the dark and cool

2 mL urine + 13 mL scintillator

2 mL urine distillate

C

Fig. 12. The scheme of urine sample preparation by D method

Fig. 13. The scheme of urine sample preparation by E method

The performance test result can be seen in Figure 14 and 15 for tritium concentration in the urine of 0.5 Bq/mL and 1 Bq/mL, respectively. They indicate that the E method has the highest eficiency with the average of 35% and 58% for tritium concentration of 0.5 Bq/mL and 1 Bq/ mL. In the F method that is direct LSC measurement, the tritium activity is not detected in the recovered urine as the same as with those for A and B method. The separation procedure shown in Figure 10-13 is carried out using distillation apparatus shown in Figure 5 in section 2.2.

For tritium measurement in the urine the E method is used. The 24 h urine sample is collected in a plastic bottle, and about 25 mL of the sample is added with 1.25 mg of active charcoal, shaked vigorously for about 30 minutes, then filtered using filter paper to obtain clear and colorless filtrate that free of particulate matter. The filtrate is then again added with active charccoal and distilled completely at 70 oC to eliminate the yellow color of the first filtrate that can alter measurement using LSC device (Puhakainen et al., 2007; Momoshima et al, 1986). The distilate obtained is then added with 1.5 g KMnO4 and 0.05 g NaOH to destruct the urine organic compound, and again distilled completely at 70 oC. The distillate is then added with 0.125 mL concentrate sulfuric acid to destruct carbonate compound resulted from previous reaction. The CO2 released from the reaction is then flushed out by nitogen gas flow for about 10 minutes.

Fig. 14. The method efficiency of 0.5 Bq/mL urine sample preparation. Number 1 represents the F method, numbers 2-6 represent the A – E method.

The Separation of Tritium Radionuclide from

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Indonesian), *Proc. of National Seminar on Science and Nuclear Technology*, ISSN 1858- 3601, Nuclear Technology Center for Materials and Radiometry of National

concentration in urine (in Indonesian), *Proc. of National Seminar on Science and Nuclear Technology*, ISSN 1858-3601, Research Center for Nuclear Technique of

Fig. 15. The method efficiency of 1 Bq/mL urine sample preparation. Number 1 represents the F method, numbers 2-6 represent the A – E method.

### **3. Conclusion**

As tritium naturally is present in environmental material, human is normally exposed internally with tritium via foods, drinking water, inhaled air, and also skin absorption. The tritium in the human body contributes radiation doses that affecting human health, hence the monitoring of tritium concentration in the environmental samples becomes interesting to avoid tritium intake by human.

This chapter has described the environmental sample preparation needed in tritium monitoring. Several developed distillation techniques in the preparation of environmental sample including air, water, soil, grass and urine have indicated a good performance result. Nevertheless, the sample preparation method for environmental tritium measurement is still interested to be developed to obtain the better performance. It is hoped that the chapter is technically worth in solving environmental and health problems arise in this industrial era.

#### **4. References**

Bhatt, A.R., Greenhalgh, R., Ortel, C.P. 2002. Determination of tritium in urine samples and validity of results, Idaho National Engineering and Environmental Laboratory.

Glastone, S., Jordan, W.H. 1980. *Nuclear Power Reactor and Its Environmental Effects,* American Nuclear Society, 0-89448-024-3, La Grange Park, Illinois.

Fig. 15. The method efficiency of 1 Bq/mL urine sample preparation. Number 1 represents

As tritium naturally is present in environmental material, human is normally exposed internally with tritium via foods, drinking water, inhaled air, and also skin absorption. The tritium in the human body contributes radiation doses that affecting human health, hence the monitoring of tritium concentration in the environmental samples becomes interesting to

This chapter has described the environmental sample preparation needed in tritium monitoring. Several developed distillation techniques in the preparation of environmental sample including air, water, soil, grass and urine have indicated a good performance result. Nevertheless, the sample preparation method for environmental tritium measurement is still interested to be developed to obtain the better performance. It is hoped that the chapter is technically worth in solving environmental and health problems arise in this industrial

Bhatt, A.R., Greenhalgh, R., Ortel, C.P. 2002. Determination of tritium in urine samples and validity of results, Idaho National Engineering and Environmental Laboratory. Glastone, S., Jordan, W.H. 1980. *Nuclear Power Reactor and Its Environmental Effects,* American

Nuclear Society, 0-89448-024-3, La Grange Park, Illinois.

the F method, numbers 2-6 represent the A – E method.

**3. Conclusion** 

era.

**4. References** 

avoid tritium intake by human.


Trivedi, A., Galeriu, D., Lamoth, E.S. 2000. Dose contribution from metabolized organically

United Nations. 1988. *Sources, effects and risks of ionizing radiation: United Nations Scientific* 

*annexes*. United Nations Publication, Sales No. E.88.IX.7. New York . US Environmental Protection Agency, Radioactivity in drinking water, EPA Report 570/9- 81-002 (Office of Drinking Water (WH-550), Washington DC), 1981.

7.

bound tritium after chronic tritiated water intakes in human. *Health Phys*., 78, pp. 2-

*Committee on the Effects of Atomic Radiation. Report to the General Assembly, with* 
