Introduction
In the field of petroleum exploration, traditional gamma-gamma density (GGD) logging technology has played a crucial role for many years [1-5]. However, the growing awareness of environmental protection has made the risks of pollution and operational safety associated with GGD technology increasingly apparent, posing challenges for its further development. In this context, neutron-gamma density (NGD) logging technology has attracted attention owing to its advantages of environmental protection and controllability [6-10]. GGD relies on the transport of monoenergetic gamma rays from the source to the detectors, whereas NGD is based on the transport of neutron-induced gamma rays whose energy exhibits uncertainty. In NGD, the gamma rays detected by the detector are influenced by neutron transport from the neutron source to the point of the gamma-ray-producing neutron interaction in the formation and by the subsequent transport of the gamma rays from their source to the gamma-ray detector. The influence of thermal neutron effects was eliminated by conducting density measurements using inelastic gamma rays produced by high-energy neutrons [11, 12]. The emitted neutrons undergo inelastic scattering reactions with the isotopes of crucial elements in the medium within a few microseconds, producing inelastic gamma-rays. These gamma rays are less influenced by neutron transport, enabling them to reflect the formation characteristics more accurately and increasing their suitability for density measurements. However, evaluating inelastic gamma-rays can be difficult because they depend on both neutron and gamma physics and simultaneously undergo multiple physical processes. Hence, entanglement between the neutron and gamma transport increases the complexity of the measurement and its sensitivity to the environment. The generation and attenuation of inelastic gamma rays are directly influenced by environmental factors such as lithology, porosity, and fluid properties. Understanding both the neutron and gamma physics pertaining to changing environments is critical for developing an accurate method for NGD technology [13-15].
NGD technology has been actively developed over the past few decades. For instance, Odom et al. used inelastic gamma rays for density measurements, which was based on the neutron-gamma coupled field [16, 17]. However, this method was affected by neutron transport, and neutron transport corrections must be considered in subsequent studies. Jacobson et al. developed a correction technique that employed the captured gamma count ratio to obtain a compensated inelastic gamma ratio, thereby achieving density measurements [18]. Zhang et al. developed a density method that used the inelastic gamma count ratio and fast neutron count to avoid neutron correction [19]. Luycx et al. approximated the initial inelastic gamma flux by using fast neutron counts for density measurements [20]. Wang et al. created a correction model utilizing epithermal neutrons and divided the inelastic gamma ray energy spectrum into high- and low-energy windows to reduce the influence of pair production [21]. Additionally, Zhang et al. introduced an adaptive method for obtaining inelastic gamma spectra during environmental changes and an integrated capture correction for density measurements [22]. While these studies have made progress, researchers have primarily focused on analyzing the neutron transport process and less on the dynamic changes during gamma attenuation. Inelastic gamma rays generated by neutron-induced reactions exist in formations with a non-monoenergetic distribution, whereas chemical sources such as Cs-137 generate monoenergetic gamma rays in a homogeneous manner. Furthermore, typical neutron-induced gamma rays can reach energies of up to 8 MeV [23]. Pair production must be considered because of its vital role in the neutron-induced gamma transport process. These factors increase the complexity of gamma attenuation. Previous NGD and GGD measurements provided possibilities for density measurements. However, most previous NGD methods considered the mass attenuation coefficient as a constant, which limited the accuracy because it was closely related to the formation composition. In this study, we introduce the mass attenuation coefficient as a function related to the formation lithologies and pore contents to accurately depict the intricate interaction mechanisms between radiation and formation, which is essential for obtaining an accurate formation density. Additionally, this provides a new approach to complement previous methods.
The remainder of this paper is organized as follows. Section 2 introduces the method and presents the development process. In addition, a pulsed neutron density tool that was subsequently employed for concept verification is described. Section 3 presents the results for the different simulated scenarios and demonstrates the effectiveness of the method. Finally, conclusions are presented in Sect. 4.
Method
The development of the method is shown in Fig. 1: Box1 reviews the coupled field theory of NGD measurements, which is the foundation for the proposed method because it depicts the distribution of inelastic gamma rays. Box2 is the key to the method. A function for the mass attenuation coefficient is developed, which is then used to derive the density. Certain key parameters, such as the hydrogen index that cannot be directly expressed in this mathematical form, are obtained through tool measurements. Box3 presents an analysis of the physical parameters using a real NGD tool during the development stage. Extensive Monte Carlo simulations are conducted to establish a quantitative relationship between the detector responses and physical parameters of the formation, which is utilized to obtain these key parameters. Finally, the density is calculated.
_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-F001.jpg)
Coupled field theory of NGD measurement
NGD logging technology relies on inelastic gamma rays to measure the formation density [24-29]. The distribution of inelastic gamma-rays involves two interconnected links between neutrons and gamma transport [30-32], as described below.
The pulsed neutron source emitted 14 MeV fast neutrons. According to the neutron diffusion theory, the distribution of fast neutrons in a spherical model can be described as follows:_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M001.png)
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_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M004.png)
Assuming that the source distances of the near- and far-gamma detectors are L1 and L2 (L1<L2), respectively, the following equations are obtained:_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M005.png)
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_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M009.png)
Development of the NGD method
The attenuation of gamma rays in formations is closely linked to the formation density and mass attenuation coefficient. The attenuation is primarily influenced by various physical processes, including the photoelectric effect, Compton effect, and pair production. The Compton effect and pair production are the primary factors that affect the attenuation of high-energy gamma rays. Thus, the total attenuation coefficient μm can be expressed as_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M010.png)
According to the principles of the Compton effect and pair production [35, 36], their mass attenuation coefficients can be expressed as_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M011.png)
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According to the preceding analysis, treating the mass attenuation coefficient as a function of the environmental parameters is expected to better depict the gamma formation reaction sensitivity and improve the accuracy of NGD calculations. Thus,_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M014.png)
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_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M016.png)
After substituting the mass attenuation coefficient μm from Eq. 14 into Eq. 8, the equation can be rewritten as_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M017.png)
Analysis of physical parameters using NGD tool
Geant4, an open-source Monte Carlo platform, was used for simulations. The tool model (Fig. 3) had a total length of 2328 mm and diameter of 188 mm and featured four neutron detectors and two gamma detectors. A boron-containing shield was positioned at the base of the neutron detectors to minimize the impact of water in the mud pipe on neutron detection. Additionally, the near-gamma detector was used for density measurement and for formation sigma and elemental measurements. A two-layer shielding structure was implemented to reduce interference from the captured gamma rays generated by the interaction of the tool with thermal neutrons. A cubic space measuring 6 m × 6 m × 6 m, with a borehole diameter of 215.9 mm, was designed to simulate the formation environment. The tool was positioned at the center of the borehole. This tool is currently under construction and will be deployed in the field upon completion. Therefore, it was selected for verifying the feasibility of the proposed method.
_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-F003.jpg)
Extensive simulations were conducted using an NGD tool model that incorporated various formation lithologies (limestone, sandstone, and dolomite) and porosity ranges (0 p.u. to 40 p.u.). These simulations aimed to establish the relationship between the detector responses and relevant physical parameters in Eq. (17) and therefore, will be used for concept validation. The specific relationships are:
(a) Hydrogen index (IH)
The correlation between the hydrogen index and detector responses was analyzed using the simulation data. Figure 4 presents the correlation coefficients between the various detector responses and hydrogen index. These coefficients measure the strength of the linear relationship between variables, with values closer to 1 indicating a strong correlation. This analysis helps identify the optimal response for representing the hydrogen index. The features represent various detector counts: FN1 and FN2 correspond to near- and far-fast neutron counts; ENT1 and ENT2 correspond to near- and far epithermal neutron counts; and CAP1 and CAP1 correspond to near- and far-capture gamma counts. In addition, RFN, RETN, and RCAP represent the respective ratios of fast neutrons, epithermal neutrons, and capture gamma counts. As shown in the figure, the ratio of the near-to-far epithermal neutron counts
_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-F004.jpg)
(b) Formation density (ρ)
To accurately represent the formation density, correlation analysis was applied to evaluate the relationships between the various detector responses and density. In the figure, IN1 and IN2 represent the near and far inelastic gamma counts, respectively, whereas CAP1 and CAP2 represent the near and far capture gamma counts, respectively. RIN is the ratio of the near-to-far inelastic gamma counts and is given by RIN=IN1/IN2. In addition, RCAP is the ratio of the near-to-far capture gamma counts. RIN exhibits the strongest correlation with density, which makes it optimal for describing the density in Eq. (9) and is consistent with the principles of NGD physics [38, 39].
(c) Formation macroscopic atomic number (Z)
The macroscopic atomic number Z, which is an inherent characteristic of the formation, is strongly influenced by the lithology and pore content. By analyzing the detector counts within a specific energy window (0.07–0.35 MeV), denoted as Nlith, a relationship can be established to represent the macroscopic atomic number. As shown in Fig. 4, this method allows the derivation of Z from the detector responses, using counts within the designated energy range to effectively characterize the macroscopic atomic number of the formation.
In summary, the density, hydrogen index, and formation macroscopic atomic number Z can be represented using RIN, RETN and _2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M018.png)
_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M019.png)
Results and discussions
To prove the effectiveness of developing mass attenuation coefficient function, we compared two approaches for treating the mass attenuation coefficient: as a constant versus as a function of formation composition. The results demonstrated that treating it as a function significantly enhanced the calculation accuracy, thereby highlighting the effectiveness of the method. Next, we assessed the performance of the method across various environments, focusing on the formation lithology and pore content. Finally, we considered three test cases to validate the applicability of this method to complex formations. The absolute errors were used to evaluate the calculated density results, as expressed in Equation 19. The calculated results were considered accurate when the absolute errors were less than the threshold of 0.025 g/cm3 [40]._2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M020.png)
Comparison of the two approaches regarding the mass attenuation coefficient
Section 2.2 emphasizes that the proposed method treats the mass attenuation coefficient as a function pertaining to the formation lithology and pore content. To evaluate the effectiveness of this method, a comparison was conducted that primarily focused on two approaches regarding the mass attenuation coefficient: treating it as a constant (denoted as h) versus treating it as a function. Based on Eq. (8) and the analysis of the relevant physical parameters in Sect. 2.3, the following equation is obtained if the mass attenuation coefficient is treated as h:_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-M021.png)
Limestone with densities ranging from 2.018 g/cm3 to 2.862 g/cm3 was designed to compare the two approaches. Figure 5 shows the absolute density errors of both approaches. Significant differences were observed. The constant method exhibits a relatively high average absolute error of 0.048 g/cm3, whereas the error calculated by the proposed method is reduced by approximately four times compared with that of the constant method, with an average absolute error of 0.012 g/cm3. This demonstrates the effectiveness and accuracy of the new method for measuring the formation density.
_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-F005.jpg)
Pore content impact analysis
In NGD measurements, neutron transport is sensitive to the presence of pore content. To evaluate the effect of different pore contents on the accuracy of this method, limestone with porosities ranging from 0.9 p.u. to 40 p.u. was selected, with pores filled with water, gas, or oil. The density results for different pore contents are presented in Table 1 and Fig. 5.
| Porosity (p.u.) | Water (1.0 g/cm3) |
Gas (0.2 g/cm3) |
Oil (0.835 g/cm3) |
|---|---|---|---|
| 0.9 | 0.010 | 0.003 | 0.005 |
| 10 | 0.005 | 0.007 | 0.019 |
| 20 | 0.002 | 0.003 | 0.007 |
| 25 | 0.003 | 0.012 | 0.020 |
| 30 | 0.006 | 0.011 | 0.010 |
| 35 | 0.008 | 0.011 | 0.012 |
| 40 | 0.008 | 0.005 | 0.012 |
Table 1 and Fig. 5 present the density calculation results for various pore contents. For the analysis, seven porosity types were selected and tested under conditions in which the pores were filled with water, oil, and gas. In limestone with water-filled pores, the Hydrogen Index IH is equivalent to the porosity of the formation. The results indicate that IH minimally affects density measurements. Regardless of IH variations, the errors between the calculated and true densities were less than the threshold of 0.025 g/cm3, demonstrating that the densities calculated using the proposed method were consistent with the true densities. In addition, this method achieved accurate measurements for high IH formations. A comparison of the density calculations for different pore contents indicated that the absolute density errors were relatively small and remained below 0.015 g/cm3 when the pores were filled with water or gas. However, the errors were relatively large when the pores were filled with oil. Notably, if the pores were filled with water, oil, or gas, the absolute errors were less than 0.02 g/cm3. Thus, the method accurately determined the formation density for various porosities and pore contents.
Analysis of the effect of Lithology
Because different lithologies affect neutron transport and gamma attenuation, 42 models, including limestone, sandstone, dolomite, and one-to-one mixture of any two lithologies, were designed to verify the accuracy of the proposed method. All the model pores were filled with water, with porosities ranging from 0.9 p.u. to 40 p.u. The densities calculated using the proposed method were compared with the true densities used in simulated model construction, which varied between 1.93 g/cm3 and 2.843 g/cm3. The density results are presented in Fig. 5 and Table 2.
| Porosity (p.u.) | Limestone (g/cm3) | Sandstone (g/cm3) | Dolomite (g/cm3) | |||
| True density | Error | True density | Error | True density | Error | |
| 0.9 | 2.682 | 0.010 | 2.682 | 0.011 | 2.843 | 0 |
| 10 | 2.527 | 0.005 | 2.485 | 0.011 | 2.767 | 0.001 |
| 20 | 2.358 | 0.002 | 2.320 | 0.011 | 2.674 | 0.001 |
| 25 | 2.273 | 0.003 | 2.238 | 0.009 | 2.488 | 0.002 |
| 30 | 2.188 | 0.006 | 2.155 | 0.007 | 2.395 | 0.001 |
| 35 | 2.103 | 0.008 | 2.073 | 0.005 | 2.209 | 0.010 |
| 40 | 2.018 | 0.008 | 1.990 | 0.009 | 2.116 | 0.003 |
| Porosity (p.u.) | Limestone+Sandstone (g/cm3) | Limestone+Dolomite (g/cm3) | Sandstone+Dolomite (g/cm3) | |||
| True density | Error | True density | Error | True density | Error | |
| 0.9 | 2.658 | 0.011 | 2.763 | 0.019 | 2.739 | 0.007 |
| 10 | 2.506 | 0.011 | 2.601 | 0.016 | 2.580 | 0.004 |
| 20 | 2.339 | 0.019 | 2.423 | 0.004 | 2.404 | 0.007 |
| 25 | 2.255 | 0.005 | 2.334 | 0.005 | 2.316 | 0.014 |
| 30 | 2.172 | 0.003 | 2.245 | 0.011 | 2.229 | 0.020 |
| 35 | 2.088 | 0.005 | 2.156 | 0.015 | 2.141 | 0.006 |
| 40 | 2.004 | 0.014 | 2.067 | 0.006 | 2.053 | 0.007 |
To verify the effect of lithology on density measurements, the present study focused on a single lithology (clean formations) and mixed lithology comprising sandstone, limestone, and dolomite. Table 2 shows slight differences in the density results across various lithologies, and the average absolute error in the mixed lithology is slightly larger than that in the single lithology, possibly owing to the complexity of the composition of the formation. Regardless of whether it was a single or mixed lithology, the calculated densities were consistent with the true densities, and the absolute density errors were less than 0.02 g/cm3. Overall, the average absolute error in the test database was 0.009 g/cm3, confirming the accuracy of the proposed method for different lithologies.
Multi-parameter impact analysis
The above results quantitatively analyze the impact of lithology and pore content on the accuracy of the density measurement. To further evaluate the proposed method, three cases (Cases 1, 2, and 3) were designed, representing three lithologies (limestone, sandstone, and dolomite) and three pore contents (water, oil, and gas), while considering the mud components (such as chlorite). Specifically, Case 1 simulates water-filled limestone with 20% chlorite; Case 2 simulates oil-filled sandstone with 10% chlorite; and Case 3 simulates dolomite-containing gas with a relatively high chlorite content of 40%. In all these cases, the borehole size was 8.5 in, with a porosity range set from 0 p.u. to 25 p.u., and formation densities between 2.211 g/cm3 and 2.712 g/cm3. The results are shown in Fig. 6.
_2026_01/1001-8042-2026-01-9/alternativeImage/1001-8042-2026-01-9-F006.jpg)
The inelastic gamma and epithermal neutron ratios varied across formations with different lithologies and pore contents, highlighting the effect of formation composition on neutron transport and gamma attenuation. In particular, cases 1 and 2 exhibited smaller measurement errors, demonstrating higher accuracy. In contrast, Case 3 exhibited relatively higher measurement errors, possibly because of its more complex formation composition, characterized by elevated mud content and gas-filled pores. Nevertheless, the absolute density errors in all three cases remained below 0.02 g/cm3, demonstrating the accuracy and reliability of the proposed method for measuring the formation density.
Tool calibration
Owing to the scarcity of commercial tools worldwide, the experimental validation of the NGD tool is briefly discussed in this work using Schlumberger’s work, which introduces an NGD calibration process [40]. The step-by-step process is summarized as follows:
Step 1: Preparation for calibration. A large water-filled calibration tank was used. Access to the aluminum sleeve and the ability to control the fluid in the mud channel (air or water) were ensured.
Step 2: Performing multiple distinct measurements. Measurements across a wide dynamic range were performed under designated configurations: with aluminum sleeve and water in the mud channel, with aluminum sleeve and air in the mud channel, without aluminum sleeve and water in the mud channel, and without aluminum sleeve and air in the mud channel.
Step 3: Fitting a linear model and evaluating the fit The best linear fit was applied to the calibration data points. χ2 was calculated to assess the goodness of the fit.
Step 4: Repeatability Check. The calibration process was repeated multiple times without altering the tool or setup. Consistency in the calibration gain was ascertained, particularly for critical parameters.
Step 5: Analyze and Compare. Calibration gains across repeated runs were compared to ensure the reliability of the calibration process.
The multiple configurations employed in this approach effectively established a set of measurement boundary conditions. This design enhanced the dynamic range of the detector count rates and improved the calibration accuracy. The calibration process considers the unique characteristics of NGD tools and can be extended to future NGD tools. Further research, along with calibration and field data acquisition, is planned to validate the practical utility of the proposed method after the development of a new version of the NGD tool.
Conclusion
A new mass attenuation coefficient function of formation lithology and pore content was introduced. Based on the study of the neutron-induced gamma attenuation process, the mass attenuation coefficient was found to vary according to the formation parameters. Therefore, it may be considered as a function to better evaluate the effects of environmental variables on gamma attenuation.
A new density measurement method was developed by employing the concept of mass attenuation coefficient function that evaluated the effects of formation composition on gamma attenuation. The method employed inelastic gamma rays for density measurement while incorporating epithermal neutrons to correct for neutron transport, for example, the influence of fast neutrons on the spatial distribution and intensity of inelastic gamma rays. The proposed method integrated information from both neutrons and gamma rays to accurately evaluate interaction mechanisms between radiation and formation and obtain precise density measurements.
An elaborate NGD tool model was developed and employed to verify the performance of the proposed method. The proposed method was evaluated using 63 sets of simulated models of varying lithologies and pore contents. The results showed that the absolute errors of the densities calculated using the proposed method were below 0.02 g/cm3 for all the cases. Specifically, the same level of accuracy was achieved in mixed cases, proving its effectiveness. Therefore, this can provide theoretical support for designing new NGD tools.
The proposed method faces challenges under extreme environmental conditions and tool calibration. For example, under logging-while-drilling downhole conditions, such as high temperature (150 °C) and high pressure (2000 psi), the performance of the detectors and electronics of the tool may be affected. In addition, the physical properties of borehole fluids may change, thus affecting measurement accuracy. Furthermore, this method relies significantly on calibration coefficients, which requires high-level calibration standards in tool-specific environments. Further research is required to improve the applicability of the proposed method.
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