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TOWARDS ENVIRONMENTAL – FRIENDLY ADDITIVES FOR 
SULPHIDE SCAVENGING IN OIL AND GAS DRILLING 
OPERATIONS 
Mutiu K. Amosa 
Guest Consultant (R&D/HSE) 
Yusran Technical Services Limited 
Port-Harcourt, Nigeria
Introduction 
 Drilling Fluids 
 Drill Stem 
 Scavengers 
 Health, Safety and Environmental (HSE) 
Considerations
Introduction (Contd.) 
Figure 1: The circulating system for a mud Figure 2: Cuttings transport in 
the annulus
Theory 
 Sour gas has been reported in old fields where the 
presence of hydrogen sulphide had not been 
previously reported (Carter et al, 1979). 
 The most HSE compliant scavenger in drilling fluids so far 
is magnetite. This scavenger has a limitation of low 
reaction rates in high pH but faster rates in low pH muds 
(Garrett et al, 1979, KMC Oiltools, 2006). 
 Whereas muds’ pH are not usually allowed to go below 9.5. 
It is usually between 10 and 11.5 (M-I, LLC, 2001). 
 Although commercial Zinc-containing compounds (ZCCs) 
are very effective but pose rheological and environmental 
problems (Ray et al, 1979). 
 Zinc metal has been classified as a toxic substance, 
concentrations as low as 0.15 ppm contamination could be 
potentially hazardous, hence, rendering the ZCCs as 
environmentally non-viable (Martin, 2005).
 Efficiencies of some organic compounds like Acrolein, 
Formaldehyde, and chelates like EDTA, NTA etc as 
sulphide scavengers have been reported. Their 
reactions with H2S are too complex to be predicted, 
and besides, there are outstanding questions 
concerning HSE, especially the health aspects of 
reactants and reaction products of the organic 
compounds/chelates. Formaldehyde has been clearly 
confirmed to be carcinogen (Nasr-El-Din et al, 2002). 
 These organic compounds and chelates usually 
renders themselves easily for sweetening purposes 
rather than application in muds (Sitz et al, 2003).
Theory (contd.) 
Description of An Ideal Scavenger 
An Ideal Scavenger has to meet the following 
requirements (Garrett et al, 1979): 
 Complete, fast, and irreversible reaction with H2S 
under all mud conditions; 
 Should be able to undergo a quantitative reaction with 
sulphide; 
 pH stability of up to and beyond 11.5; 
 Non-corrosive to metals; 
 Easy and safe to handle and non-polluting to the 
environment; 
 Non detrimental to mud’s rheology; 
 Must have a good environmental acceptability before 
and after reaction with sulphide.
 Complexes of iron in the Fe2+ oxidation state are usually 
less sensitive to pH values (Shriver et al, 1999). 
 Fe2+, ferrous ion is a necessary trace element used by all 
known living organisms. It is also used in fertilizing aquatic 
plants (Anonymous, 2007). 
 Gluconic acid is generally recognised as safe (GRAS). Also, 
sodium, calcium and iron salts of gluconic acid have been 
confirmed mild, non-volatile, non-corrosive and non-toxic. 
They are stable up to alkaline pH values and are also stable 
at high temperatures. A metal gluconate is comparatively 
better than EDTA, NTA and other chelators 
(Ramachandran et al, 2006). 
 Most metal gluconates are confirmed HSE compliant 
materials especially the iron, sodium, zinc and calcium 
salts of gluconic acids which are used for medicinal 
purposes in both humans and animals (Ramachandran et 
al, 2006). 
 The inhibitive effect of calcium gluconate on carbon steel 
in neutral aqueous media has been put to test due to its 
non-toxic and eco-friendly nature and found satisfactory 
(Shibli and Kumary, 2004).
H2S Stability and pH 
H2S  H+ + HS-  2H+ + S2-……………….……..………………..….(1) 
Effects of H2S on Oil-well steel 
H2S + Fe2+ → FeS + 2H+..............................................................(2) 
 At the anode: Fe → Fe2+ + 2e- …………………………………….…….. (3) 
 At the cathode: 2H+ + 2e- → H2 …………………………..………………..(4) 
Probable reactions of the scavengers with sulphides: 
Synthetic Magnetite (Fe3O4) 
Fe3O4 + 6S2- → 3FeS2 + 4O2- …………………………………………………..(5) 
Ferrous Gluconate 
Fe (C6H12O7)2 + S2- → FeS + 2 [C6H12O7]- …(6) 
Ferrous gluconate + Sulphide →Ferrous sulphide + gluconate
Experimental 
Materials and Instruments 
Commercially available ferrous gluconate and 
magnetite were used as scavengers. The water based 
mud used is saturated brine mud. Analar grade 
reagents of Potassium hydroxide, HCl, sodium 
sulphide pellets were used. Instruments such as pH 
meter (model OMEGA PHH-3X), Agitator (model 
INBS 3000), Chemetrics Vacuettes Kit (Vacuettes K- 
9510B), Filter Paper (Whatman No. 50), Fann 
Viscometer (Fann 35A Model) and the API Filter Press 
were used during the experiments.
Experimental (Contd.) 
Procedure (Chen et al (1985), Ray et al (1979)) 
Na2S 
Scavenger 
Brine at pH 12 Agitation 
Settling & Filtration 
Residue 
Filtrate 
Figure 3: Procedure for the desulphurization tests 
Sulphide 
Content 
Determination
Results and Discussion 
Desulphurization Tests 
750 
700 
650 
600 
550 
500 
450 
400 
350 
300 
250 
200 
150 
100 
50 
0 
Gluconate at 25 deg. C Gluconate at 35 deg. C Gluconate at 45 deg. C Gluconate at 55 deg. C 
Magnetite at 25 deg. C Magnetite at 35 deg. C Magnetite at 45 deg. C Magnetite at 55 deg. C 
0 20 40 60 80 100 120 140 
Sulphide Content in Mud,mg/l 
Time Taken, mins 
MAGNETITE 
FERROUS GLUCONATE 
25 deg. C 
35 deg. C 
45 deg. C 
55 deg. C
Results and Discussion 
Rheology Tests
Conclusions 
 Ferrous gluconate can be used in a wide range of mud pH 
values. It provides efficient desulphurization as the mud 
was tested “zero-sulphide” content after the 
desulphurization tests. This indicates that it can protect 
operating personnel from the toxic H2S. Magnetite was 
only able to remove about 30 % of the sulphide from the 
mud. 
 Ferrous gluconate generally has no adverse effect on mud 
properties, even at larger concentrations. It can even serve 
as a rheology modifier in muds. Magnetite in larger 
concentrations can cause unwanted weight additions to the 
mud. 
 Ferrous gluconate has the advantages of being more readily 
available and cheaper than synthetic magnetite.
Recommendations 
 This information needs to be translated into realistic 
rig-site hydrogen sulphide scavenging tests. 
 More research should be conducted on the existing 
organic products to identify their true scavenging 
capabilities under realistic wellbore drilling 
conditions. 
 Optimization of the scavenging processes of the 
ferrous gluconate should be looked into.
ACKNOWLEDGEMENT 
 MEMBERS OF STAFF AND MANAGEMENT OF 
THE MI-SWARCO DRILLING FLUID 
ENGINEERING COMPANY, PORT-HARCOURT, 
RIVERS STATE. 
 ENGRS. MUAZU MAGAJI AND BASHEER BELLO 
OF SHELL PETROLEUM DEVELOPMENT 
COMPANY - SPDC (EAST), PORT-HARCOURT, 
RIVERS STATE. 
 CHEMICAL ENGINEERING DEPARTMENT, 
AHMADU BELLO UNIVERSITY, ZARIA.
THANK YOU

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Towards environmental – friendly additives for sulphide scavenging in oil and gas drilling operations

  • 1. TOWARDS ENVIRONMENTAL – FRIENDLY ADDITIVES FOR SULPHIDE SCAVENGING IN OIL AND GAS DRILLING OPERATIONS Mutiu K. Amosa Guest Consultant (R&D/HSE) Yusran Technical Services Limited Port-Harcourt, Nigeria
  • 2. Introduction  Drilling Fluids  Drill Stem  Scavengers  Health, Safety and Environmental (HSE) Considerations
  • 3. Introduction (Contd.) Figure 1: The circulating system for a mud Figure 2: Cuttings transport in the annulus
  • 4. Theory  Sour gas has been reported in old fields where the presence of hydrogen sulphide had not been previously reported (Carter et al, 1979).  The most HSE compliant scavenger in drilling fluids so far is magnetite. This scavenger has a limitation of low reaction rates in high pH but faster rates in low pH muds (Garrett et al, 1979, KMC Oiltools, 2006).  Whereas muds’ pH are not usually allowed to go below 9.5. It is usually between 10 and 11.5 (M-I, LLC, 2001).  Although commercial Zinc-containing compounds (ZCCs) are very effective but pose rheological and environmental problems (Ray et al, 1979).  Zinc metal has been classified as a toxic substance, concentrations as low as 0.15 ppm contamination could be potentially hazardous, hence, rendering the ZCCs as environmentally non-viable (Martin, 2005).
  • 5.  Efficiencies of some organic compounds like Acrolein, Formaldehyde, and chelates like EDTA, NTA etc as sulphide scavengers have been reported. Their reactions with H2S are too complex to be predicted, and besides, there are outstanding questions concerning HSE, especially the health aspects of reactants and reaction products of the organic compounds/chelates. Formaldehyde has been clearly confirmed to be carcinogen (Nasr-El-Din et al, 2002).  These organic compounds and chelates usually renders themselves easily for sweetening purposes rather than application in muds (Sitz et al, 2003).
  • 6. Theory (contd.) Description of An Ideal Scavenger An Ideal Scavenger has to meet the following requirements (Garrett et al, 1979):  Complete, fast, and irreversible reaction with H2S under all mud conditions;  Should be able to undergo a quantitative reaction with sulphide;  pH stability of up to and beyond 11.5;  Non-corrosive to metals;  Easy and safe to handle and non-polluting to the environment;  Non detrimental to mud’s rheology;  Must have a good environmental acceptability before and after reaction with sulphide.
  • 7.  Complexes of iron in the Fe2+ oxidation state are usually less sensitive to pH values (Shriver et al, 1999).  Fe2+, ferrous ion is a necessary trace element used by all known living organisms. It is also used in fertilizing aquatic plants (Anonymous, 2007).  Gluconic acid is generally recognised as safe (GRAS). Also, sodium, calcium and iron salts of gluconic acid have been confirmed mild, non-volatile, non-corrosive and non-toxic. They are stable up to alkaline pH values and are also stable at high temperatures. A metal gluconate is comparatively better than EDTA, NTA and other chelators (Ramachandran et al, 2006).  Most metal gluconates are confirmed HSE compliant materials especially the iron, sodium, zinc and calcium salts of gluconic acids which are used for medicinal purposes in both humans and animals (Ramachandran et al, 2006).  The inhibitive effect of calcium gluconate on carbon steel in neutral aqueous media has been put to test due to its non-toxic and eco-friendly nature and found satisfactory (Shibli and Kumary, 2004).
  • 8. H2S Stability and pH H2S  H+ + HS-  2H+ + S2-……………….……..………………..….(1) Effects of H2S on Oil-well steel H2S + Fe2+ → FeS + 2H+..............................................................(2)  At the anode: Fe → Fe2+ + 2e- …………………………………….…….. (3)  At the cathode: 2H+ + 2e- → H2 …………………………..………………..(4) Probable reactions of the scavengers with sulphides: Synthetic Magnetite (Fe3O4) Fe3O4 + 6S2- → 3FeS2 + 4O2- …………………………………………………..(5) Ferrous Gluconate Fe (C6H12O7)2 + S2- → FeS + 2 [C6H12O7]- …(6) Ferrous gluconate + Sulphide →Ferrous sulphide + gluconate
  • 9. Experimental Materials and Instruments Commercially available ferrous gluconate and magnetite were used as scavengers. The water based mud used is saturated brine mud. Analar grade reagents of Potassium hydroxide, HCl, sodium sulphide pellets were used. Instruments such as pH meter (model OMEGA PHH-3X), Agitator (model INBS 3000), Chemetrics Vacuettes Kit (Vacuettes K- 9510B), Filter Paper (Whatman No. 50), Fann Viscometer (Fann 35A Model) and the API Filter Press were used during the experiments.
  • 10. Experimental (Contd.) Procedure (Chen et al (1985), Ray et al (1979)) Na2S Scavenger Brine at pH 12 Agitation Settling & Filtration Residue Filtrate Figure 3: Procedure for the desulphurization tests Sulphide Content Determination
  • 11. Results and Discussion Desulphurization Tests 750 700 650 600 550 500 450 400 350 300 250 200 150 100 50 0 Gluconate at 25 deg. C Gluconate at 35 deg. C Gluconate at 45 deg. C Gluconate at 55 deg. C Magnetite at 25 deg. C Magnetite at 35 deg. C Magnetite at 45 deg. C Magnetite at 55 deg. C 0 20 40 60 80 100 120 140 Sulphide Content in Mud,mg/l Time Taken, mins MAGNETITE FERROUS GLUCONATE 25 deg. C 35 deg. C 45 deg. C 55 deg. C
  • 12. Results and Discussion Rheology Tests
  • 13. Conclusions  Ferrous gluconate can be used in a wide range of mud pH values. It provides efficient desulphurization as the mud was tested “zero-sulphide” content after the desulphurization tests. This indicates that it can protect operating personnel from the toxic H2S. Magnetite was only able to remove about 30 % of the sulphide from the mud.  Ferrous gluconate generally has no adverse effect on mud properties, even at larger concentrations. It can even serve as a rheology modifier in muds. Magnetite in larger concentrations can cause unwanted weight additions to the mud.  Ferrous gluconate has the advantages of being more readily available and cheaper than synthetic magnetite.
  • 14. Recommendations  This information needs to be translated into realistic rig-site hydrogen sulphide scavenging tests.  More research should be conducted on the existing organic products to identify their true scavenging capabilities under realistic wellbore drilling conditions.  Optimization of the scavenging processes of the ferrous gluconate should be looked into.
  • 15. ACKNOWLEDGEMENT  MEMBERS OF STAFF AND MANAGEMENT OF THE MI-SWARCO DRILLING FLUID ENGINEERING COMPANY, PORT-HARCOURT, RIVERS STATE.  ENGRS. MUAZU MAGAJI AND BASHEER BELLO OF SHELL PETROLEUM DEVELOPMENT COMPANY - SPDC (EAST), PORT-HARCOURT, RIVERS STATE.  CHEMICAL ENGINEERING DEPARTMENT, AHMADU BELLO UNIVERSITY, ZARIA.