alexa The Effect of Produced Water from Heglig Oil Field on Chemical Additives for Fracturing Fluids

ISSN: 2380-2391

Journal of Environmental Analytical Chemistry

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The Effect of Produced Water from Heglig Oil Field on Chemical Additives for Fracturing Fluids

Fatima A Elbrir*
Department of Petroleum Engineering, College of Petroleum Engineering and Technology, Sudan University of Science and Technology, Khartoum, Sudan
*Corresponding Author: Fatima A Elbrir, Department of Petroleum Engineering, College of Petroleum Engineering and Technology, Sudan University of Science and Technology, Khartoum, Sudan, Tel: +249(0)122924771, Email: [email protected]

Received Date: Mar 26, 2018 / Accepted Date: Apr 10, 2018 / Published Date: Apr 19, 2018

Abstract

Produced water is the water produced with oil or gas during well production as a result of different operations. Recently, many Sudanese oil fields suffer from the massive amount of water production; the most water production problems in Sudan were observed in Heglig oilfield. The Heglig oilfield is located in Muglad Basin in the southeast and middle of Block 2 in Sudan. The oil production from Heglig oilfield was reported to have peaked in 2006, however it has been declined now and the water cut was reached 95%. Due to many environmental impacts, several studies were conducted for treating the produced water from Heglig oilfield to be used in irrigation; no work was presented to study the effect of Heglig oilfield produced water on chemical additives for fracturing fluids. However, this work analyzes and treats the produced water from Heglig oilfield and evaluates the possibility of the treated water for the re-using in water base fracturing fluids. Samples were collected from two different ponds in the field and analysed according to the American Public Health Association (APHA) and the results were compared with (National Recommended Water Quality (EPA)) to identify the required treatments for the collected water. The analysis was done in Rheine Waal University of Applied Science-Kamp-Lint fort-Germany. In this study, the effect of produced water from Heglig oil field on fluid formulation was studied as management processes of produced water prior to reuse for petroleum operation (Hydraulic Fracturing and Injection) or to be safe in environment. The pH effect on fluids viscosity was investigated for (6, 7, 8, 9 and 10). The results showed that the cross-linking ability of the fracturing fluid presented that better cross-linking system were achieved with 0.48 g CMHEC at pH of 8 and temperature of 40°C for HEC and 60°C CMHEC.

Keywords: Produced water; Fracturing fluids; Cross-linking system

Abbreviations

HEC: Hydroxyethyl Cellulose; CMHEC: Carboxymethyl Hydroxyethyl Cellulose; TSS: Total Suspended Solid; TDS: Total Dissolved Solids.

Introduction

Produced water is the natural water or formation water is always found together with petroleum in reservoirs [1]. Other definition of “Produced water” is water trapped during subsurface formations which is brought to the surface along with oil or gas [2]. Sometime called “flowback water” if it is brought from fluid injected into the well or reservoir at high pressure as part of a hydraulic fracturing (frac) operation [3]. It is slightly acidic and sits below the hydrocarbons in porous reservoir media extraction of oil and gas leads to a reduction in reservoir pressure, and additional water is reservoir water layer to maintain hydraulic pressure and enhance oil recovery. Produced water has a complex composition, but its constituents can be broadly classified into organic and inorganic compounds [2-5] including dissolved and dispersed oils, grease, heavy metals, radionuclides, treating chemicals, formation solids, salts, dissolved gases (including CO2 and H2S), scale products, waxes, microorganisms and dissolved oxygen[5-8]. Cations and anions play a significant role in the chemistry of produced water [9]. Produced solids could cause serious problems during oil production. For example, common scales and bacteria can clog flow lines, form oily sludge and emulsions which must be removed [10]. For Heglig Oilfield, as case study the amount of water production or water cut reach to 95% from total hydrocarbon fluids, making oil production non-economic. Therefore, the objective of this paper is to study the effect of produced water from Heglig oil field on chemical additives for fracturing fluids. Scale deposition is one of the most important and serious problems that inflict oil field water injection systems. Scale limits and sometimes blocks oil and gas production by plugging the oil producing formation matrix or fractures and perforated intervals. It can also plug production lines and equipment and impair fluid flow.

Field background

Heglig oil field is one of the largest fields of oil and gas deposits in Sudan. It has been the site of conventional petroleum production for more than one decade (since 1999), but recently it has become producing water exceed the economic range (Figures 1 and 2). Heglig field is located in southeast and middle of Block 2B, Muglad Basin, discovered by Chevron. It consists of 10 fields (Heglig main, Toma, El Bakh, El Full, Laloba, Kanga, Barki, Hamra, Simbir East and Rihan). A general structure which follows average distance between fields is about 3 to 5 km. 8 layers are developed i.e., Aradeiba main, Aradeiba B, Aradeiba E, Aradeiba F, Bentiu-1, Bentiu-2 and Bentiu-3 and Abu Gabra. First FDP was carried out in 1998. Last FDP was carried out in 2011. Field development started in June 1999 with development of 29 wells i.e., Heglig main (17), Toma (4), Barki (3) , Hamra (2), El FulI (2) wells and El Bakh (1) well.

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Figure 1: Heglig field background – production performance.

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Figure 2: Total water production from 1999 up to 2013.

Experimental work

Produced water from Heglig oil field

Sample collection: Produced water samples were obtained from the Heglig oil field (Table 1). Sample has been taken from two different ponds; the first pond presents the untreated water, while the second pond presents the water after the final field treatments with bioremediation project. Samples were taken using sterile bucket and stored in sterile containers of different sizes (1 L and ½ L) and has been kept in 4°C. This water have been experimentally measured before treatment in order to define its components such as Total Suspended Solids (TSS), Total Dissolved Solids (TDS), oil and grease, bacteria and metals. The characterization has been done using methods of testing available in Sudan and Germany in order to evaluate the compatibility of proposed treated water with hydraulic fracturing additives and formation water, in order to eliminate any problems that may cause by incompatibility.

Parameters Raw water (mg/l) Treated water (mg/l) Acceptable range (mg/l) Comments
pH 8.9-9.5 8.3-8.6 6-8 Hydration
Oil and grease 250-300 30-50 Zero Fluid stability
Total Dissolved Solids (TDS) 2662 3217 300 Hydration
Total Suspended Solids (TSS) 982 378 Zero Well plugging
Conductivity (µmhos/cm) 2.7 3.2 - -
Chloride 20 14 <2-00 Fluid stability
Sodium 575 678 Zero Scaling
Silica 11.8 11.8 <1 Crossling
Potassium 12.77 14.03 Zero Scaling
Calcium 7.193 8.19 Zero Scaling
Heavy Metals (ppm)        
Aluminium (Al) 21.6 0.2871 - -
Cadmium (Cd) <0.0009 <0.0009 - -
Chromium (Cr) 0.0158 <0.0013 - -
Copper (Cu) 0.0249 0.0249 - -
Cobalt (Co) 0.0013 0.0013 - -
Iron (Fe) 12.17 12.17 Zero Crossling/hydration
Lead (Pb) <0.0150 <0.0150 - -
Manganese (Mn) 0.1052 0.0049 - -
Nickel (Ni) 0.0155 0.0127 - -
Zinc (Zn) 0.066 0.0474 - -
Boron (Br) 0.01 0.01 Zero Scaling
Mercury (Hg) ND ND - -
Phosphorus <0.001 ND - -
Cadmium (Cd) ND ND - -

Table 1: Physical and chemical properties of water sample.

Water sampling preparation

The following tests were conducted to determine the main components and their proportion that could be found.

Total Suspended Solids measurement (TSS): A volume of produced water was measured according to APHA standard methods. Filter was carefully removed using filtration apparatus and transferred to an Aluminium weighing dish in order to reduce high dissolved solids. It was then dried for 1 h at 103°C to 105°C in an oven, cooled in desiccator to balance temperature and weighed and the TSS content was calculated in ppm (mg/l) as:

Total Suspended Solids (TSS)=a-b × 1000/sample volume (ml) (1)

Total Dissolved Solids measurement (TDS): TDS solids and electric conductivity was measured using conductivity meter (Jenway 4320), 50 ml for two samples were used.

Oil and grease measurement: Oil and grease was extracted following APHA standard methods. A measured volume of the sample (V=250 ml) was introduced into separating funnel and 1.5 ml of HCl 1:1 was added. 7.5 ml of n-Hexane was added to the acidified sample and shaken for 2 min. When it reached the equilibrium the organic layer of oil and hexane was separated in evaporating dish. Then this step was replicated 2 times more and all the separated organic layer was transferred into a pre-weighed (W1 (gm)) flask and hexane was evaporated in a water bath at 103°C to 105°C for 1 h. The flask is reweighed (W2 (gm)) and the oil and grease content is calculated in ppm (mg/l) as:

a-b/sample volume (ml) × 106 (2)

Preparation of hydraulic fracturing fluid with HEC and CMHEC

During the fracturing fluids process, a viscous non Newtonian fluid was applied to the formation with three major functions:

Delivering pressure to create fracture network and geometry within simulated zone.

Transporting proppant into the created fracture to maintain fracture conductivity.

Control of fluid leak off into the formation by forming a filter cake on the walls of the fracture.

Fracturing fluid was prepared by blending a hydratable polymer into an aqueous fluid. The aqueous fluid could be distilled water, untreated produced water, treated produced water (by process conducted in site of the Heglig oil field). In the case of batch mixing, the hydratable polymer and the aqueous fluid are blended for a period of time sufficient to form a hydrated solution.

Two types of hydratable polymers useful in the present study of cellulose derivatives Hydroxyethyl Cellulose (HEC) and Carboxymethyl Hydroxyethyl Cellulose (CMHEC), may be all of the hydratable were used and are well known to those in the well service industry.

Rheological properties and testing

Out of a hydration study, polymer powder was added to 100 ml of different types of water with stirring in a Waring® blender (medium rate that was enough to generate a slight vortex) to make up the desired concentration. According to Vo [11], the following series tests were conducted.

In the first test, the aqueous solution contained HEC was prepared by adding different concentration of powder ranged from 2.5 to 5 gram per 100 ml of tap water in order to obtain stock solution. A solution containing buffer for adjusting pH, the quantity of polymer was hydrated (starrier) in 1 L of untreated produced water for about 30 min. The solution was divided into 200 ml aliquots in beaker glasses. Aliquots were mixed with a speed of 1500 rpm to get vortex. The samples were placed into constant temperature and the viscosities measured by proRheo R 180 rheometer with concentric cylinder.

In the second series of the tests, the same polymer concentrations in the first series were used. The aqueous solution was prepared according to same procedure described in the first series. The tests were conducted at different temperatures ranged from 10 to 80°C with aqueous solutions which were thickened with 2.5-5 g of HEC cellulose per 100 ml of solution. Viscosities were determined with a proRheo R 180 rheometer.

In the third series of the tests, the effect of various pH on the viscosity of an aqueous solution thickened with two types of cellulose per 100 ml of solution was tested and the procedures were repeated.

Lastly, in fourth series of the tests, the effect of shear rates on the viscosity was investigated. All the above procedures were used for both the types of polymer.

Viscosity of fracturing fluids

Viscosity was measured several times to show continuous loss of viscosity with time at simulated down hole temperature range from 10 to 80°C and constant shear rates 300 sec-1 and several time with different pH and constant shear rates and sometimes with different shear rates.

The viscosity of the fracture fluids is very important. The fluid should be viscous enough (normally 50-1000 cp) to create a wide fracture (normally 0.2-1.0 in) and transport the propping agent into the fracture (normally 10 s to 100 s of feet) (Department of Energy, 2004).

Cross-linking system of the polymer

The cross-linking system of the present study for water based well fracturing fluids comprises of a mixture of Aluminium ion constituent with a Boron constituent. The boron constituent was selected from the group consisting Sodium tetraborate and mixtures thereof.

The liquid cross-linking system was prepared by first dissolving the Boron constituent. Aluminium ions are then added and mixed thoroughly. A water based fracturing fluid can be prepared which comprises of water, the cross-linking system described and a hydratable polymer capable of gelling in the presence of cross-linking system. The hydratable polymer useful in the present study can be any hydratable cellulose derivatives CMHEC and HEC. The water based fracturing fluid can be prepared for use by adding three types of water such as deionized water, raw water and treated water in site of the field. Borate cross-linked was used (0.5-2.0%) by weight of polymer according to Patent (US5806597).

The water based fracturing fluid prepared contained about 5 to 7g of hydratable polymer per 100 ml of water used for HEC cellulose derivative and most 0.48 g per 100 ml of water for CMHEC cellulose derivative.

Results and Discussion

Fracturing fluid rheology at different conditions

The fracturing fluid was formulated with oilfield produced water before and after treatment. The rheological properties of fracturing fluid tested are evaluated at various expected treating temperatures, shear rates and pH. A viscosity performance of cross linked-HEC, CMHEC designed with typical oilfield produced formation water at temperature range of 10 to 80°C and shear rates range of 300 to 1000 sec-1 the results are reported as follows (Figures 3-11).

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Figure 3: Rheology studies of 5 g HEC using three samples of water (pH=7.2), ambient temperature and 300 sec-1.

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Figure 4: Rheology study of HEC at ambient temperature and 300 sec-1 100% untreated formation water pH=8.5.

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Figure 5: HEC viscosity at different temperature without crosslinker.

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Figure 6: The effect of cross-linker on HEC at different temperature.

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Figure 7: The effect of cross-linker on CMHEC at different temperature using treated water.

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Figure 8: Rheology study of HEC at ambient temperature and 300 sec-1 100% untreated water.

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Figure 9: Rheology study of HEC at ambient temperature and 300 sec-1 100% treated water (on site the field).

environmental-analytical-chemistry-cross-linked

Figure 10: Rheology study of cross-linked CMHEC at ambient temperature and 300 sec-1 100% untreated water.

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Figure 11: Rheology study of cross-linked CMHEC at ambient temperature and 300 sec-1 100% treated water (on site of the field).

Conclusion

In this study, fracturing fluids formulation with three types of water was prepared. Borate and Aluminium ion with cellulose derivatives (HEC and CMHEC) in aqueous solution were investigated by using rheological measurements. The evolution of viscoelastic properties of the borate solutions and the Ammonium ion mixtures separately were characterized and the cross-linking kinetics was determined. The results indicate that the development of the cross-linking network is highly dependent on the borate concentration while the cellulose derivatives concentration is relatively unimportant. The effects of pH, temperature, shear rates and cellulose derivatives dosage on fluids formulation were systematically investigated. Optimal reaction conditions for formulation were obtained (pH: 6 and 8; temperature: >80°C; 5 g polymer dosage).

Acknowledgement

The authors would like to thank the organization of German Academic Exchange Service (DAAD) for financial assistance (Internal scholarship) at the Rheine Waal University of Applied Science (Germany) for its technical support.

References

Citation: Elbrir FA (2018) The Effect of Produced Water from Heglig Oil Field on Chemical Additives for Fracturing Fluids. J Environ Anal Chem 5: 237. DOI: 10.4172/2380-2391.1000237

Copyright: © 2018 Elbrir FA, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

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