1. Introduction

GEP

Journal of Geoscience and Environment Protection

2327-4336

Scientific Research Publishing

10.4236/gep.2020.87003

GEP-101578

Articles

Earth&Environmental Sciences

Soil Gas Radon Measurement for Identifying Active Faults in Thua Thien Hue (Vietnam)

Pham

Tich Xuan

¹Nguyen

Anh Duong

²Vu

Van Chinh

¹Pham

Thanh Dang

¹Nguyen

Xuan Qua

¹Nguyen

Van Pho

Institute of Geophysics, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Institute of Geological Sciences, Vietnam Academy of Science and Technology, Hanoi, Vietnam

14072020

0807446426, May 202017, July 2020 20, July 2020

2014

This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/

The solid-state nuclear track detectors have long been applied to assess the activity of tectonic faults. We measured the Radon ( Rn) concentration in soil gas on 09 profiles with a total of 245 measurement points in Thua Thien Hue area (Vietnam). Measurement results show that the Rn concentration in soil gas ranges from ~10 Bq/m ³ to 144,570 Bq/m ³. There is a clear difference in the Rn concentration on the granite rock of Dai Loc complex compared to the remaining rocks. The calculated background value and anomaly threshold of Rn concentration on the granite rock of Dai Loc complex and on the remaining rocks are 33,488 Bq/m ³, 82,839 Bq/m ³ and 5313 Bq/m ³, 24,850 Bq/m ³ respectively. Spatial distribution of Rn concentration in soil gas reflects the existence of faults since Rn concentration increases at the points above or near fault lines. The level of expression of fault activity is assessed by radon activity index ( KRn), which is calculated by the ratio of anomaly value to background value of Rn concentration. According to KRn, in Thua Thien Hue area, only the Dakrong-Hue fault shows a strong expression of activity with high and very high KRn (the maximum KRn = 27.21). The Truong Son, Huu Trach River, Ta Trach River and Bo River fault zones do not show clear activity with low and medium KRn. There is no Rn anomaly value recorded on the Rao Trang fault, demonstrating that it is likely to be inactive at present. The study results indicate that the Rn concentration in soil gas is a strong evidence of the existence of faults or tectonic fracture zones as the Rn concentration always increases at the points above or near the fault line.

Radon Active Fault Radon Activity Index Thua Thien Hue Vietnam

1. Introduction

Measurement of Rn concentration in soil gas has long been applied to detect tectonic faults (King et al., 1996). Increasingly, this method is widely used in fault study and particularly effective in determination of active faults as well as studies on earthquake (e.g., King, 1978; Al-Hilal & Al-Ali, 2010; Baubron et al., 2002; Font et al., 2008; Ghosh et al., 2009; González-Díez et al., 2009; Haerudin et al., 2013; Hauksson, 1981; Ioannides et al., 2003; Lombardi & Voltattorni, 2010; Papastefanou, 2010; Richon et al., 2010; Seminsky & Demberel, 2013; Utkin & Yurkov, 2010; Wakita et al., 1980; Walia et al., 2008; Wang et al., 2014). The results of these studies indicate the existence of tectonic faults recorded by anomalies of Rn concentration. Accordingly, on fault lines or in fault zones, the Rn concentration in soil gas is usually high and the anomaly value often appears. This anomaly value depends on the nature, activity level and geological characteristics of the fault. However, the existence of Rn concentration anomalies in soil gas is not an irrefutable evidence of active fault. In order to determine the active fault through Rn concentration, many criteria have been used, from qualitative extrapolation to classification of Rn concentration anomalies into levels corresponding to activity levels of fault. One of these efforts belongs to Seminsky & Demberel (2013). These authors proposed the radon activity index (K_Q) which is the ratio of the maximum Rn concentration (Q_max) to the Rn concentration outside the fault zone. These authors also classified the radon activity index into five levels: low, medium, increased, high and ultra-high, which correspond to the activity levels of fault.

In Vietnam, the method of soil gas radon measurement has been successfully applied in determining active faults in many regions such as Northwest region, Thac Ba, Son La and Song Tranh 2 hydropower plants and proposed locations of Ninh Thuan 1 and 2 nuclear power plants in Vietnam (Tran Van Duong & Tran Trong Hue, 1996; Tran Trong Hue, 1996, 1999; Nguyen Van Pho & Nguyen Trong Yem, 1996; Nguyen Van Pho & Hoang Tuyet Nga, 1996; Nguyen Van Pho et al., 1999, 2004; Pham Tich Xuan et al., 2017). Pham Tich Xuan et al. (2017) proposed calculating the radon activity index (K_Rn) based on the ratio of anomaly value of Rn concentration to anomaly threshold value and inherited the classification of radon activity index from Seminsky & Demberel (2013) as mentioned above.

Thua Thien Hue province is located in Central Vietnam that possesses the complicated geological structure and is divided by tectonic faults such as Truong Son, Nam O-Nam Dong, Dakrong-Hue (Figure 1). This is the result of collision between the Indian-Australian plate and the Eurasian plate, which formed the strike-slip fault system from Myanmar to the study area in Cenozoic (Tapponnier et al., 1982; Lacassin et al., 1997; Morley, 2004; Yin, 2010; Nguyen Anh Duong et al., 2013). Although the seismic hazard is not as high as that of the countries located directly on the plate boundary such as Japan, the Philippines and Indonesia, this area is at risk of strong earthquakes with magnitude greater than 6 in tectonic fault zones (Nguyen Dinh Xuyen et al., 2004; Le Huy Minh et al., 2015). Therefore, the assessment of activity of tectonic fault zones is an essential task for the analysis of seismic hazard in the study area. In this study, we have determined the level of expression of fault activity by using solid-state nuclear track detector. Radon concentration is measured on 9 profiles with a total of 245 measurement points in Thua Thien Hue area. Our analysis involves newly available, unpublished Rn data for the study area. The activity of fault is then assessed by radon activity index K_Rn. The result of activity of tectonic fault zones will be the essential information for the seismic hazard analysis in the study area.

2. Geological Characteristics

The study area is located in the northwest of Hue city, including some areas of A Luoi, Phong Dien, Huong Thuy, Nam Dong, Huong Tra districts and Hue city (Figure 1). This area consists of the mountainous terrain in A Luoi district with an average height of 600 - 800 m and a peak of 1774 m, and the midland terrain including low hills and mountains with an average height of 100 - 200 m and coastal plain. According to the Geological and Mineral Resources Map (1994) of Vietnam on scale of 1:200,000 the study area is composed of Late Proterozoic-Early Paleozoic metamorphic sedimentary rocks, Paleozoic sedimentary rocks, Late Neogene-Early Quaternary terrigenous sediments and undivided Quaternary unconsolidated sediments (Figure 1). Late Proterozoic-Early Paleozoic metamorphic sedimentary rocks are composed of crystalline schists distributed in narrow strips in the southwest near the Laos border. Paleozoic sedimentary rocks occupy the majority of study area, consisting of silty sandstone, shale, andesite effusive rock, limestone and marl. Pliocene-lower Quaternary sediments are comprised of pebble, breccia, grit, sand and clay, limitedly distributed along the Ta Trach River. Undivided Quaternary unconsolidated sediments consist of pebble, breccia, sand and silt mainly distributed in the northeast along the coast and rivers.

Among magmatic rocks, the granitoid rocks predominate, including gneisogranite, granodiorite, biotite granite, two-mica granite, which are classified into Dai Loc (ργaD1dl), Ben Giang-Que Son (γδPZ₃bg-qs), Hai Van (ργaT₃hv) and Ba Na (γP2bn) complexes. Additionally, there also exist small gabbroic and gabbro-pyroxenitic intrusive bodies belonging to Nui Ngoc (υμPZ₁nv) and Cha Val (νaT₃cv) complexes with limited outcrop area.

In the study area, tectonic faults develop in different directions, among which the northwest-southeast, sub-latitudinal and sub-longitudinal faults predominate (Figure 1). The main faults include:

The first-order Truong Son fault in this area consists of a major fault and a minor fault (Truong Son sub-fault). This fault system develops in northwest-southeast direction and runs through the southwest of study area in A Luoi district. The fault dips southeastwards with a relatively steep angle of about 70˚ - 80˚.

The second-order Nam O-Nam Dong fault is a branch fault of Truong Son fault, which follows northwest-southeast direction in the western part and sub-latitudinal direction in the eastern part. The northwest-southeast segment (the western part) has a nearly vertical dip angle, while the sub-latitudinal segment (the eastern part) dips southwards with an angle of 70˚ - 80˚.

The third-order Dakrong-Hue fault runs in the sub-latitudinal direction through Hue city and extends to the East Sea. The Dakrong-Hue fault dips towards the north-northeast with an angle of 65˚ - 70˚.

The fourth-order and higher-order faults include a series of small faults such as Huu Trach River, Ta Trach River, Bo River, Rao Trang faults, etc. with different directions. The Huu Trach River fault runs along the Huu Trach River, follows northwest-southeast direction in the north from the intersection with the Dakrong-Hue fault, and changes to sub-longitudinal direction in the south (Figure 1 and Figure 2). The Ta Trach River fault runs in northwest-southeast direction, along the Ta Trach River in the northeast of study area. The Bo River fault develops in sub-longitudinal direction from the intersection with the Dakrong-Hue fault to the south and crosses other faults such as Rao Trang, Nam O-Nam Dong faults and Truong Son sub-fault. The Rao Trang fault runs in west northwest-east southeast direction through the center of study area.

3. Data and Methodology

The Rn concentration in soil gas was measured by using solid-state nuclear track detectors (SSNTDs). Film-detectors DOSIRAD LR115 (type 2P, serial number 5058180) with size of 1.5 × 1.5 cm were used and calibrated in the standard radon chamber with known Rn concentration to determine detector efficiency (E) of the method. Film-detectors were glued to the bottom of plastic cups, which were then covered with thin PE film (~50 µm) to filter ²²⁰Rn and prevent water penetration. At each measurement point, the plastic cup containing film-detector was placed face-down in the bottom of the pit of 25 cm diameter and 50 cm depth.

The pit was covered by oil-paper with supporting bamboo bars and backfilled with soil to avoid radon loss and rain (Figure 2). The average measurement time was 5 days, and the time of placing and collecting detectors was carefully recorded to the minute. The collected film-detectors were carefully preserved in plastic bags for further treatment. At each detector location, the radiation intensity in the pit bottom was measured by radiometer СРП 88Н (Russia) to eliminate accidental accumulations near the surface of radioactive elements.

In the laboratory, film-detectors were chemically etched in 2.5M NaOH solution for 90 minutes at a temperature of 60˚C which was maintained constant by the thermostat HAAKE-D8. After etching, film-detectors were washed and blotted. The density of tracks was automatically counted on specialized equipment. The Rn concentration was calculated by using the following equation (Nidal et al., 2007):

C R n = D NET t ⋅ E ( Bq ⋅ m − 3 ) (1)

where C_Rn—Rn concentration in soil gas; D_NET—density of tracks counted on film-detectors (track∙cm⁻²); t—time of placing detectors in the field; E—detector efficiency of the method. Etching, track counting and radon concentration measurement were carried out at the Institute of Nuclear Science and Technology (Hanoi).

The data were processed by statistical method; background value and anomaly threshold were determined by boxplot method (Reimann et al., 2005).

The Rn concentration was measured on 9 profiles with a total of 245 measurement points. The measurement profiles were determined with the help of geologists to ensure that they cross the fault lines. However, the actual locations of the profiles depend on specific field conditions (such as terrain, water bodies, rivers, streams, soil-rock characteristics, etc.), so most of the profiles are not straight line. The distance between detector locations was 25 - 30 m. This distance was chosen based on the migration ability of Rn in soil gas (Barnet et al., 2008) in order that anomalies (if any) can be detected with reasonable cost. The locations of measurement points were determined by a handheld GPS device-GPSmap 60CSx. The distribution of the profiles is presented in Figure 3.

4. Results and Discussion4.1. Background Concentration and Anomaly Threshold

Measurement results show that Rn concentration in soil gas ranges widely from 10 Bq/m³ to 144,570 Bq/m³. Some statistical parameters of Rn concentration are shown in Table 1 and Figure 4. The distribution of dataset of Rn concentration approximates to log-normal distribution.

The soil gas Rn concentrations on the profiles are also different. The TTH1 profile has a higher Rn concentration than the others in terms of the minimum, maximum and average values (Table 2). The Rn distribution and concentration

Table 1 Statistical parameters of soil gas radon concentrations in the Thua Thien Hue area (Bq/m3)

	Valid N	Median	Mean	Minimum	Maximum	Std.Dev.
Rn	245	3605.5	3388.4	10.0	144,570.0	18,628.7

Table 2 Distribution of Rn concentration (Bq/m3) according to measurement profiles

Profile	Valid N	Mean	Minimum	Maximum	Std. Dev.
TTH1	23	37,830	12,460	133,351	28,284
TTH2	30	9046	624	52,401	10,941
TTH3	33	4099	10	35,085	7314
TTH4	22	4655	295	29,479	7415
TTH5	30	5137	205	22,042	6383
TTH6	22	5320	392	16,532	4870
TTH7	19	6895	194	35,849	9747
TTH8	32	13,438	790	41,826	11,446
TTH9	34	15,694	32	144,570	30,842

in soil gas are influenced by physical, chemical, geological and climatic factors (Peake & Schumann, 1993), in which the concentration of radioactive elements (²³⁸U, ²²⁶Ra) and soil permeability are the most important factors. The Rn concentration in soil gas is usually increased along tectonic faults, probably because tectonic faults often create destructive zones increasing the soil permeability. The concentration of radioactive elements is related to the lithological properties of rock. Normally granite rocks (and also granite pegmatite) are thought to contain the higher concentration of radioactive elements compared to other rocks, therefore the soil gas Rn concentration in distribution area of these rocks is usually higher than in the area of other rocks. In the study area, the TTH1, TTH4 and TTH6 profiles are located in the outcrop area of granitoid rocks, in which the TTH1 profile is located on granitoid rocks of Dai Loc complex (ργaD₁dl) including two-mica porphyritic gneissogranite, melanocratic gneissogranite, granite pegmatite, granite aplite, meanwhile the TTH4 and TTH6 profiles are located on granite rocks of Ben Giang-Que Son complex (γδPZ₃bg-qs) consisting of gabbrodiorite, diorite, granodiorite, horblende-biotite granite (Figure 2). However, only the Rn concentration on TTH1 profile is significantly higher and different from that on TTH4, TTH6 and remaining profiles. This difference is due to lithological properties of underlying rocks. Therefore, in order to calculate thresholds of background and Rn concentration anomalies, the TTH1 profile needs to be examined separately to eliminate the influence of lithological factors. Although TTH4 and TTH6 routes, profiles are distributed on granite rocks, the pattern of Rn concentration is similar to that of other profiles, so they can be investigated together with the others.

By applying boxplot method (Reimann et al., 2005), the threshold of Rn background concentration was determined to be 24,850 Bq/m³ for the dataset excluding TTH1 profile, meanwhile this value on TTH1 profile was 82,849 Bq/m³ (Figure 5). Once the thresholds of background have been determined, all values within range of thresholds belong to the background data set, and then the Rn background concentration is the arithmetic mean of the whole dataset after excluding anomaly values (exceeding thresholds). Thus, in the study area two background values can be accepted, one for TTH1 profile and the other for remaining profiles. For TTH1 profile, values within range of ≤82,849 belong to background dataset and the Rn background concentration is 33,488 Bq/m³. For remaining profiles, values within range of ≤24,850 Bq/m³ belong to background dataset and the Rn background concentration is 5313 Bq/m³. Using the determined thresholds of 82,849 Bq/m³ and 24,850 Bq/m³ for TTH1 profile and remaining profiles respectively, 18 anomaly points of Rn concentration were identified (Table 3). It

Table 3 Anomalies of radon concentrations and Radon Activity Index (KRn) of Thua Thien Hue area

	Meas. points	Rn content (Bq/m³)	Error (Bq/m³)	K_Rn
1	TTH.1-20	133,351	±850	3.98
2	TTH.9-04	49,557	±567	9.33
3	TTH.9-05	97,468	±795	18.35
4	TTH.9-06	144,570	±969	27.21
5	TTH.9-07	33,505	±466	6.31
6	TTH.9-08	30,592	±446	5.76
7	TTH.9-09	58,663	±617	11.04
8	TTH.9-17	26,898	±419	5.06
9	TTH.8-03	31,289	±460	5.89
10	TTH.8-09	26,067	±420	4.91
11	TTH.8-17	30,066	±452	5.66
12	TTH.8-22	27,932	±435	5.26
13	TTH.8-32	41,826	±533	7.87
14	TTH.2-12	34,291	±436	6.45
15	TTH.2-29	52,401	±540	9.86
16	TTH.3-26	35,085	±437	6.60
17	TTH.4-01	29,479	±435	5.55
18	TTH.7-11	35,849	±491	6.75

can be seen from Table 3 that the Rn concentration anomalies are mostly detected on TTH9 profile (7 points) and TTH8 profile (5 points). The TTH1, TTH2, TTH3, TTH4 and TTH7 profiles have 1 to 2 anomaly points, whereas no anomaly points are found on TTH5 and TTH6 profiles.

4.2. Relationship between Radon Concentration and Activity of Fault

The radon concentration in soil gas depends on many factors, but mainly on geological characteristics and tectonic activity of the region. Therefore, the absolute values of radon concentration in soil gas in different regions may be dissimilar or even significantly dissimilar. There are many systems for classification of radon concentrations in soil gas radon mapping. In Germany, Kemski et al. (2001) divided Rn concentration into 4 categories: 1) low (<10 kBq/m³), 2) medium (10 - 100 kBq/m³), 3) increased (100 - 500 kB/m³) and 4) high (>500 kB/m³). Meanwhile, the 3-category scale was used in Hong Kong: 1) low (<10 kBq/m³), 2) medium (10 - 100 kBq/m³) and 3) high (>100 kBq/m³) (Tung et al., 2013). The classifications of concentration levels using absolute values of soil gas Rn concentrations mentioned above are based on the criteria for human health and ecological environment protection and only used in soil gas radon mapping with the purpose of environmental protection.

Numerous studies (e.g., King et al., 1996; Moussa & Arabi, 2003; Ciotoli et al., 1999) have shown that radon anomalous concentrations are very sensitive to fault activity. The radon anomalous concentrations in soil gas can be many times higher than the background value depending on the activity level of fault (Wang et al., 2014; Seminsky & Demberel, 2013). Measurements of soil gas radon concentrations on several faults in different regions in the world (Richon et al., 2010) show that although the maximum Rn concentration and background value on different faults are very dissimilar, the ratio K of the maximum Rn concentration to background value on the same fault or in the same measurement area is generally quite high. This indicates that active faults make the significant difference (anomalies) in radon concentration in its range of influence compared to the background concentration.

Seminsky and Demberel (2013), when studying the relationship between the Rn concentration in soil gas and the activity of faults in Central Mongolia, proposed using the relative index of radon activity K_Q—the ratio of the maximum Rn concentration (Q_max) to the minimum Rn concentration outside the fault zone (Q_min) for classification of fault activity. Accordingly, for Central Mongolia, the fault activity is characterized by the levels of radon activity index as follows: ultra-high (K_Q > 10), high (10 > K_Q > 5), increased (5 > K_Q > 3), medium (3 > K_Q > 2) and low (K_Q < 2). The use of radon activity index is, in our opinion, a more objective classification compared to the scale using absolute values. However, comparing the maximum anomaly values with the concentrations outside the fault zone by the classification scheme of Semminsky & Demberel (2013) will lead to many uncertainties, for example which values are considered to be outside the fault zone and among these values, which ones should be chosen? Even if the location is determined to be outside the fault zone, how far is it from the fault so that the value can be chosen, etc. Therefore, the concentration comparison must be conducted based on a statistical basis, particularly comparing the concentration anomaly value with the background value. We suggested using radon activity index K_Rn—the ratio of anomaly value to background value of Rn concentration for classification of radon activity, which corresponds to the activity level of fault.

Based on the arguments presented above, we proposed using the classification by Seminsky & Demberel (2013) with some modifications to classify levels of radon anomalous concentration in soil gas according to radon activity index K_Rn for Thua Thien Hue area. Thus, radon activity index can be divided into 5 levels: ultrahigh (K_Rn > 20), high (20 ≥ K_Rn > 15), increased (15 ≥ K_Rn > 10), medium (10 ≥ K_Rn > 5) and low (K_Rn ≤ 5), which correspond to 5 levels of activity expression of fault (Table 4).

Based on this classification of activity levels of fault using radon activity index (K_Rn), Pham Tich Xuan et al. (2017) applied and satisfactorily explained the relationship between activity of fault and radon activity index in Thac Ba, Song Tranh 2 and Ninh Thuan hydropower plants (Vietnam).

Table 4 Classification of Radon Activity Index (KRn) and activity expression of fault

Radon activity index		Expression of fault activity
K_Rn	Level	Expression of fault activity
K_Rn > 20	Ultra-high	Fault having strong activity expression
20 ≥ K_Rn > 15	High	Fault having clear activity expression
15 ≥ K_Rn > 10	Increased	Fault having activity expression or existence of strong tectonic fracture zone
10 ≥ K_Rn > 5	Medium	Fault having not clear activity expression or existence of fracture zone
K_Rn ≤ 5	Low	Fault having no activity expression

Thac Ba hydropower plant is built on Chay River (Northern Vietnam), running along the northwest-southeast Chay River fault which is considered to be active in the present time with dextral strike-slip mechanism (Nguyen Trong Yem, 1996; Nguyen Dang Tuc, 2000). The distribution characteristics of radon concentration anomaly in Thac Ba hydropower plant have confirmed that (Pham Tich Xuan et al., 2017). In Thac Ba hydropower plant area, the anomalies of soil gas radon concentration range from 28,289 Bq/m³ to 273,133 Bq/m³ and the corresponding K_Rn values varies between 3.5 and 34.1.

Song Tranh 2 hydropower plant was built on Tranh River in Central Vietnam. Since the reservoir impoundment in early 2012, earthquakes have frequently occurred in this area. They were identified as triggered earthquakes due to impoundment (Le Huy Minh et al., 2015). The strongest earthquake with magnitude of 4.7 occurred on November 15, 2012. Soil gas radon measurement in this area showed that the maximum Rn concentration reached 77,729 Bq/m³ and the Rn concentration anomalies ranged between 3974 Bq/m³ and 77,729 Bq/m³ corresponding to K_Rn from 1.8 to 34.9.

The soil gas radon measurement conducted in Ninh Thuan is within the framework of studies on evaluating the proposed locations of nuclear power plants. This area is considered to be relatively stable in terms of tectonics. Geological-tectonic studies show that within the 8 km radius from the proposed locations of Ninh Thuan 1 and Ninh Thuan 2 nuclear power plants, there mainly exist very small tectonic fracture zones or tectonic faults which show no activity or unclear activity in the present time. The results of soil gas radon measurement indicated that the maximum Rn concentration reached 52,627 Bq/m³, the anomalies were in the range of 15,568 Bq/m³ to 52,627 Bq/m³ and K_Rn varied between 3.6 and 12.1.

The comparison between results of soil gas radon measurement in three above-mentioned areas and results of geological studies demonstrated that in Ninh Thuan area, most of anomaly points (55/57) had K_Rn ≤10, only 2 points had K_Rn of 11.3 and 12.1. It can be said that the relatively low K_Rn reflects the inactivity of faults or the anomalies in this area are only recorded in tectonic fracture zones, which increase the soil permeability, facilitating radon release, leading to high radon concentration in soil gas. This result is completely consistent with other research results in this area. In Thac Ba area, many anomaly points had relatively high K_Rn (>10) with the maximum of 33.9, demonstrating the obvious activity of Chay River fault as recorded by previous geological studies mentioned above (Nguyen Trong Yem, 1996; Nguyen Dang Tuc, 2000). Meanwhile, in Song Tranh 2 hydropower plant, the activity of faults is clearly reflected through a series of earthquakes occurring here (Le Huy Minh et al., 2015), which was confirmed by results of soil gas radon measurement. Among a total of 115 anomaly points, the levels of K_Rn were recorded as follows: K_Rn ≤ 5 (3 points); 5 < K_Rn ≤ 10 (57 points); 10 < K_Rn ≤ 15 (32 points); 15 < K_Rn ≤ 20 (12 points) and K_Rn > 20 (11 points). K_Rn > 10 accounted for nearly half of the anomaly points, indicating the clear activity expression of faults, in which the maximum K_Rn reached 94.2.

4.3. Activity Expression of Faults According to the Soil Gas Measurement Data in the Thua Thien Hue Area

As mentioned above, 18 anomaly points were determined in Thua Thien Hue area with the radon concentration ranging from 26,067 Bq/m³ to 144,570 Bq/m³ and the corresponding K_Rn varying between 3.98 and 27.21. The entire anomaly points with K_Rn > 10 are located on the Dakrong-Hue fault (on the TTH9 profile) (Table 3).

+ Truong Son fault and its minor fault (Truong son sub-fault)

The Truong Son fault is a first-order zoned fault. In the study area, it consists of a major fault and a minor fault (Figure 1 and Figure 2). On the major fault, there are two radon measurement profiles: TTH2 and TTH3, in which the TTH3 profile crosses both major and minor faults near the intersection of these two faults. On the TTH2 profile, an anomaly point TTH2-12 was recorded on the fault line with Rn concentration of 34,291 Bq∙m⁻³ and K_Rn = 6.45. On the TTH3 profile crossing Truong Son fault in the south of study area, there was only one anomaly point coinciding with the fault line (TTH3-26) with Rn concentration of 35,085 Bq/m³ and K_Rn = 6.60. Both anomaly points recorded on Truong Son fault have medium K_Rn (≤10), indicating that the activity expression of this fault is unclear in the present time, at least on A Luoi-A Dong segment (Figure 6).

There are two radon measurement profiles (TTH1 and TTH2) on the Truong Son sub-fault. On the TTH1 profile, one anomaly point which coincides with the fault line was recorded with Rn concentration of 133,351 Bq/m³ and K_Rn = 3.98. On the fault line of TTH2 profile, one anomaly point (TTH2-29) was also detected with Rn concentration of 52,401 Bq∙m⁻³ and K_Rn = 9.86. The combination graph of radon concentration distribution on the Truong Son sub-fault is presented in Figure 7. Among two anomaly points recorded on the Truong Son sub-fault, one has low K_Rn (on TTH1 profile) and another has medium K_Rn (on TTH2 profile), demonstrating that the activity expression of this fault is also unobvious as its major fault.

+ Dakrong-Hue fault

On the Dakrong-Hue fault, there is only one measurement profile TTH9 located in Phong My commune (Phong Dien district). On this profile, up to 7 anomaly points were recorded, in which the anomaly points from TTH9-04 to TTH9-09 form a series of 6 continuous points with Rn concentration from 30,592 Bq/m³ to 144,570 Bq/m³, the TTH9-17 point is located further to the north with Rn concentration of 26,898 Bq∙m⁻³. Notably, the TTH9-05 and TTH9-06 points located on the fault line have high and ultrahigh K_Rn of 18.35 and 27.21 respectively, in which the TTH9-06 point has the highest measured Rn concentration of 144,570 Bq/m³ in the study area. The K_Rn is from high to ultrahigh, indicating that the activity expression of Dakrong-Hue fault is apparent in the present time (Figure 8).

+ Huu Trach River fault

There are two radon measurement profiles TTH6 and TTH8 on this fault. 5 anomaly points were recorded, all of which are located on TTH8 profile. Among anomaly points, the TTH8-03 is located directly on the fault line with Rn concentration of 31,289 Bq/m³ and K_Rn = 5.89. The TTH8-17, TTH8-22 and TTH8-32 points are quite far from the fault line to the north with medium K_Rn ranging from 5.26 to 7.87 (Figure 9). The K_Rn on Huu Trach River fault is at medium level, demonstrating that the activity expression of this fault is unclear. The inactivity of this fault is also manifested in the complete absence of radon concentration anomalies on the TTH6 profile which crosses the southern part of this fault. It is noteworthy that the TTH8-17, TTH8-22 and TTH8-32 points are located in the quadrant of intersection of Huu Trach River fault and Dakrong-Hue fault. The occurrence of anomaly points in this area is probably due to the extension in the quadrant caused by the movement of Dakrong-Hue fault, and these anomaly points reflect the activity of Dakrong-Hue fault rather than Huu Trach River fault.

+ Ta Trach River fault

There is one radon measurement point TTH7 on the Ta Trach River fault. On this profile, only one anomaly point located on the fault line was found with Rn concentration of 35,849 Bq∙m⁻³ and medium K_Rn = 6.75. Thus, similar to the Huu Trach River fault, the activity expression of this fault is unobvious (Figure 10).

+ Bo River fault

On the Bo River fault, there is one radon measurement profile TTH4 located near the hot water source of Ngoi village in Hong Ha commune (Figure 11). Only one anomaly point (TTH4-01) was recorded at the beginning of the profile with Rn concentration of 29,479 Bq/m³ corresponding to medium K_Rn = 5.55.

Thus, according to radon measurement results, the activity expression of Song Bo fault is not apparent.

+ High-order Rao Trang fault

This is a small longitudinal fault that crosses the center of study area and is controlled by the TTH5 measurement profile. No anomaly points were detected on this profile; only the relatively considerable increase in Rn concentration was observed at some points adjacent to the fault line, however, the Rn concentration was within the range of background values. This indicates that the Rao Trang fault does not show any activity in the present time.

It is noteworthy that on all measurement profiles, with or without radon concentration anomalies, the points located above or near the fault line witnessed a relatively considerable increase in soil gas radon concentration compared to the points located further from the fault (not presented here). This demonstrates that the soil gas radon concentration is a strong evidence of the existence of faults or tectonic fracture zones as the radon concentration always increases at the points above or near the fault line.

5. Conclusion

In Thua Thien Hue area, the soil gas radon concentration varied widely from ~10 Bq/m³ to ~145,000 Bq/m³. Among the rocks present in the study area, the radon background on granite rocks of Dai Loc complex was significantly high and different from that on remaining rocks. The result of measurement profile on granite rocks of Dai Loc complex showed that the radon concentration ranged from 12,460 ± 259 Bq/m³ to 133,351 ± 850 Bq/m³ with the average value of 37,830 Bq/m³. The radon background concentration on granite rocks of Dai Loc complex was determined to be 82,849 Bq/m³. Results of other measurement profiles on remaining rocks indicated that the radon concentration ranged between ~10 Bq/m³ and 144,570 Bq/m³, and the average value varied from 4099 Bq/m³ to 15,694 Bq/m³. The radon background concentration for these rocks was 24,850 Bq/m³. Among a total of 245 measurement points, 18 anomaly points of radon concentration were detected.

The activity expression of fault was assessed using radon activity index K_Rn—the ratio of anomaly value to background value of soil gas radon concentration. The assessment results showed that among 18 anomaly points of radon concentration in Thua Thien Hue area, only 01 point had ultrahigh K_Rn (K_Rn = 27.21), 01 point had high K_Rn (K_Rn = 18.35) and 01 point had increased K_Rn (K_Rn = 11.04), all of which are located on the Dakrong-Hue fault. This demonstrates that in Thua Thien Hue area, only the Dakrong-Hue fault shows a strong expression of activity with high and very high K_Rn. Meanwhile, on the first-order zoned Truong Son fault and its sub-fault, the fourth-order and higher-order faults such as Huu Trach River, Ta Trach River and Bo River faults, some anomaly points were recorded, but K_Rn was at low and medium levels, indicating that the activity expression of these faults is unclear in the present time. Therefore, in order to clarify the activity expression of all faults, it is necessary to expand the soil gas radon concentration measurement network in the study area.

Acknowledgements

The authors would like to thank two anonymous reviewers for their helpful comments. This article is the result of the National-level Project “Research and evaluate earthquake hazard for territorial development planning, ensuring safety of hydropower projects, irrigation works and cultural relics in Thua Thien Hue province”, code: DTDL.CN.51/16.

Conflicts of Interest

The authors declare no conflicts of interest regarding the publication of this paper.

Cite this paper

Xuan, P. T., Duong, N. A., Van Chinh, V., Dang, P. T., Qua, N. X., & Van Pho, N. (2020). Soil Gas Radon Measurement for Identifying Active Faults in Thua Thien Hue (Vietnam). Journal of Geoscience and Environment Protection, 8, 44-64. https://doi.org/10.4236/gep.2020.87003

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