Patent Number: 060020636
Section: claims

1. A method for disposing of wastes by injection within a geological stratum, comprising the steps of: a) selecting an appropriate generally permeable and porous target stratum, said target stratum being overlain by a layer of relatively low permeability strata;  b) calculating the approximate total available storage volume of the target stratum, based on the approximate average thickness and area of the stratum and the average porosity of the stratum;  c) preparing an at least partly cased injection well extending from the ground surface into said target stratum;  d) positioning a pressure gauge within said injection well in the region of the base of said well for measuring liquid pressure within said well;  e) perforating the casing of said injection well in the region where the well traverses said target stratum;  f) injecting a pressurized slurry comprising waste materials suspended in a carrier liquid into said injection well in a series of discrete injection episodes separated by interinjection episodes at an injection pressure equal to or greater than the fracture or overburden pressure;  g) measuring the well bottom pressure of the slurried wastes with said pressure gauge on a substantially continuous basis during each injection and interinjection episode with said pressure gauge;  h) terminating said injection when the target stratum is generally fully saturated with slurried wastes, as determined by the amount of wastes injected and the calculated available storage volume;  said method being further characterized in that the pressure and flow rate of slurry injection during each injection episode is adjusted to maintain a generally steady state pressure level at the well bottom, as measured by the pressure gauge, each injection episode terminating when the well bottom pressure climbs a predetermined amount above said steady state level and each interinjection period terminating when said pressure drops a predetermined amount below said steady state level.  a) selecting an appropriate generally permeable and porous target stratum, said target stratum being overlain by a layer of relatively low permeability strata;  b) calculating the approximate total available storage volume of the target stratum, based on the approximate average thickness, area and mechanical compressibility of the stratum and the storage capacity according to the formula: Storage Capacity=dP/(dV.times.dt)  c) calculating the optimal injectivity for the formation according to the formula: Injectivity=Slurry Injection Rate/(Press.sub.inj -Press.sub.fmt) where Press.sub.inj =injection pressure and Press.sub.fmt =formation pressure;  d) preparing an at least partly cased injection well extending from the ground surface into said target stratum;  e) positioning a pressure gauge within said injection well in the region of the base of said well for measuring liquid pressure within said well;  f) perforating the casing of said injection well in the region where the well traverses said target stratum;  g) injecting at generally said optimal injectivity a pressurized slurry comprising said waste material suspended in a carrier liquid into said injection well in a series of discrete injection episodes at an injection pressure equal to or greater than the fracture or overburden pressure, said injection episodes separated by interinjection episodes wherein no slurry is injected and said well is shut-in;  h) measuring the well bottom pressure of the slurried wastes with said pressure gauge on a generally continuous basis during each injection and interinjection episode with said pressure gauge;  i) terminating said injection when the target stratum is generally fully saturated with slurried wastes, as determined by the amount of wastes injected and the calculated available storage volume;  said method being further characterized in that the pressure and flow rate of slurry injection during each injection episode is adjusted to maintain a generally steady state pressure level at the well bottom, as measured by the pressure gauge, each injection episode terminating when the well bottom pressure climbs a predetermined amount above said steady state level and each interinjection period terminating when said pressure drops a predetermined amount below said steady state level.  a) an initial injection of clear carrier fluid at a high selected rate to initiate hydraulic fracture of the target formation;  b) gradual introduction within said carrier liquid of an increasing concentration of waste matter over the course of a first selected time interval;  c) injection of waste-bearing slurry during a second selected time interval;  d) gradual diminishment of the waste content within said slurry, to arrive at a clear carrier liquid, over the course of a third selected time interval;  e) an interinjection period during which the well is shut-in for a fourth selected time interval;  f) a repeat of steps a-e for a selected number of times, followed by a prolonged shut-in period for a fifth selected time interval greater than said fourth time interval.  composition of waste material including mud/sand/slop/water ratios  daily slurry injection volumes  produced sand grain size during injection  fines/clay content during injection  hydrocarbon content of the sand or viscosity of the muds and slops  formation grain size and stress state  formation geology  heterogeneous effective stress and permeability distribution in the formation  repeated loading and unloading of rock stresses  wellbore cement quality  wellbore completion and quality.  transient changes in permeability and transmissivity within the target stratum;  changes in compressibility and stress state within the target stratum;  dynamic fracture propagation within the target and overburden strata;  dynamic in situ pressure and stress gradient development;  dynamic in situ pressure and stress dissipation;  target stratum deformation and yielding;  overburden straining and bending; and  asymmetric waste distribution about the injection well.  documentation of waste volumes and formation response to allow for optimization and control of the SFI process;  assessment of hydraulic isolation and containment of the waste material within the target stratum;  quantitative evaluation of formation stress state, well integrity, formation containment, formation response, in situ waste distribution, formation storage capacity, or formation infectivity during the injection process;  ensuring worker safety during the injection procedures;  evaluation of target stratum mechanical and flow responses to the injection process; and  determination of distribution of the injected material within the target stratum.  i) monitoring the slurry injection and emplacement by means of measurements of wellbottom hole pressure within the injection wells to assess formation pressure response to the waste injection, as well as permitting pressure fall-off tests and assessment of SFI and formation mechanics;  ii) monitoring wellbottom hole pressure within observation wells displaced from the injection wells within about 400 meters to provide assessment of formation pressure gradients, formation mechanics and flow of wastes;  iii) step rate injection tests conducted within the injection well, to assess fracture extension rate and formation pressure response, as well as closure stress gradient and waste containment within the formation;  iv) fluid level measurements within the offset monitoring wells to assess distribution of pressure gradients within the waste emplacement zone and to provide a measurement of waste containment;  v) tracer logs within the injection well, to determine the extent of hydraulic isolation of the formation and wellbore during the injection process and an assessment of fracture orientation within the target formation;  vi) monitoring of surface tiltmeter data generated in the region about the wellhead to assess the fracture orientation and azimuth, as well as permitting a reconstruction of fracture geometry, horizontal and vertical dimensions and spread of the waste body within the target formation and the rate of change of same, and deformation within the formation, as well as a further assessment of the SFI mechanics;  vii) injection parameter monitoring comprising real time recording of injection pressures at wellhead and wellbottom, casing pressure, injection rate, injection volumes and slurry density to permit a correlation of formation response with the SFI operating parameters;  viii) material sampling of the slurry conducted regularly and frequently to accommodate various local regulatory requirements.  maximum slurry injection rate: about 1.1-2.0 times a calculated fracture extension rate  daily slurry injection volume: about 700-1500 m.sup.3 /day  waste injection volume: about 50-225 m.sup.3 /day  av. slurry concentration: about 5-30% sand by volume  av. slurry density: about 1000-1300 kg/m.sup.3  max. slurry density: about 1375 kg/m.sup.3  injection Pressures about 1.1 to 1.5 times a calculated fracture extension pressure  injection episodes: approximately 24 hour injection/interinjection cycle, including  injection cycle: 5 day injection cycle, 2 days shut-in or 11 day injection cycle  maximum slurry injection rate: about 1.1-2.0 times a calculated fracture extension rate  daily slurry injection volume: about 700-1000 m.sup.3 /day  waste injection volume: about 50-100 m.sup.3 /day  av. slurry concentration: about 15% slop by volume  av. slurry density: about 1000-1200 kg/m.sup.3  max. slurry density: about 1250 kg/m.sup.3  injection Pressures about 1.1 to 1.5 times a calculated fracture extension pressure  injection episodes: approximately 24 hour injection/interinjection cycle, including about 4-14 hours/day injection episode  injection cycle: 5 day injection cycle, 2 days shut-in. 2. A method as in claim 1, wherein the duration of said injection episode is further determined by means of placing one or more surface uplift indicators on the ground surface in the region around said injection well and terminating said injection episode upon measurement of a fixed amount of uplift, with the duration of said interinjection episodes being determined by assessing the time of approximate cessation of further surface uplift. 3. A method as in claim 2 wherein said surface uplift indicators comprise tiltmeters positioned within about 400 meters of said injection well. 4. A method as in claim 2, wherein said surface uplift indicators are employed to localize the region of injected solids within the target stratum, by positioning an array of said indicators in the approximate region of said target stratum and localizing the area of uplift. 5. A method as in claim 1, wherein the duration of said injection and interinjection episodes is further determined thorough the use of monitoring wells located between about 50 and 400 meters from said injection well, each of said monitoring wells having a pressure gauge in the region of the bottom thereof, said injection episodes being terminated when the pressure as measured in said monitoring wells climbs by more than about 25% of the original pressure within said wells. 6. A method as in claim 1, wherein said target stratum is selected to have a minimum average thickness of approximately 4 meters, a minimum average transmissivity of approximately 0.5 Darcy-meters, a minimum porosity of about 15% in those regions that have an average permeability above about 100 milliDarcy, and a minimum compressibility of about 1.times.10.sup.-6 kPa.sup.-1. 7. A method as in claim 6, wherein said target stratum is overlain by overburden strata having a minimum thickness of about 10 meters with a maximum permeability of about 10 milliDarcy. 8. A method as in claim 1, wherein said overburden strata is selected to include clays or zeolites sufficient for the absorption of toxic organic and heavy metal wastes. 9. A method as in claim 1, comprising the further step of measuring microseismic disturbances at several locations in the region of said injection well, and assessing thereby the approximate horizontal and vertical spread of the waste solids emplacement zone within said target stratum and the extent of growth of the solids emplacement zone. 10. A method as in claim 1, comprising the further step of incorporating within said slurry a cementitious agent. 11. A method as in claim 1, wherein each injection episode commences with the injection of clear carrier liquid, with the concentration of suspended wastes increasing therein over the initial 15-30 minutes of said injection episode to reach the target concentration of said suspended wastes, with said injection episode concluding with the injection of additional clear carrier liquid, with the injection well then being shut in under full injection pressure. 12. A method as in claim 1, comprising the further step of post-injection monitoring of the target stratum to assess migration of the waste solids entombed therein from the target stratum, said post-injection monitoring comprising the measurement of surface uplift in the region of the injection well, monitoring and recording said measurements on a periodic basis, and determining thereby any instability within the solids emplacement zone and the localization of the solids emplacement zone, and comparing the said localization with the localization thereof immediately following the injection process to assess any volume change in the site or movement thereof. 13. A method as in claim 12, comprising the further step of measuring microseismic disturbances in the region about said injection well to assess thereby any instability in the solids emplacement zone and the localization thereof. 14. A method for disposing of waste material by injection within a geological stratum, comprising the steps of: 15. A method as in claim 14, comprising the further step of performing pressure fall off and step rate tests for evaluation of formation flow behavior, formation geomechanical behavior and slurry injectivity in the target formation for assessment of formation suitability for waste injection and determining a necessary approximate fracture extension rate and pressure. 16. A method as in claim 14, wherein said well casing is perforated with a perforation density of approximately 20 shots per meter, radially phased at least 90.degree. around said casing and within a perforation interval of less than about 10 meters. 17. A method is in claim 14, wherein said target stratum is selected to lie at a depth less than about 800 meters of the surface, and surface displacement is measured in the region surrounding said injection well by means of tiltmeters positioned on the surface about said well, said method comprising the further step of analyzing the data produced by said tiltmeters to reconstruct the formation fracture behavior in terms of dip, orientation and aspect ratio of the formation fractures and deformation of the target formation, namely volumetric and shear deformation. 18. A method as in claim 14, wherein said target stratum is selected to lie at a depth greater than about 800 meters, and comprising the further step of performing microseismographic analysis of the ground region about said well, and assessing thereby the vertical and areal extend of fracture propagation resulting from said injection process. 19. A method as in claim 14, wherein the step of injecting slurry into the target stratum comprises the following steps: 20. A method as in claim 19, wherein said second selected interval is 4-14 hours and the total duration of steps a-e is approximately 24 hours. 21. A method as in claim 14, wherein said slurry is prepared according to a method wherein the concentration of slurry additives (optionally including viscosifiers, surfactants and adsorbing agent), slurry viscosity, slurry waste concentrations and slurry specific gravity are selected as a function of the following considerations: 22. A method as in claim 14, wherein said waste material is selected from a viscous fluid, oil sludge, municipal waste water or water treatment sludge and industrial wastes. 23. A method as in claim 14, wherein said waste comprises wastes in particulate form having a grain size between 2 .mu.m and 1000 .mu.m and said slurry is prepared having a maximum solids concentration of about 40% by volume. 24. A method as in claim 22, wherein said slurry bearing said waste material is injected in a series of intervals alternating with intervals of injection of a slurry incorporating sand particulates. 25. A method as in claim 23, further including the steps of injecting into said well a facilitating slurry incorporating a viscous fluid prior to injection of said waste material, and a further injection of said facilitating slurry into said well when the wellbottom pressure surges above a preselected amount. 26. A method according to claim 14, wherein geomechanical and formation flow responses selected from the following are measured in said strata surrounding said injection well: 27. A method according to claim 26, wherein said selected geomechanical and formation flow measurements are used for the steps selected from the following: 28. A method as claimed in claim 14, wherein said waste material injection is accompanied by one or more monitoring procedures conducted before, during and after the injection process, selected from among the following: 29. A method as in claim 14, comprising the further step of incorporating within said slurry particulates comprising between approximately 50% to 95% shale chips or clays. 30. A method as in claim 29, wherein said slurry further includes low or medium level radioactive wastes. 31. A method as in claim 14, wherein said target stratum is overlain by overburden consisting of alternating relatively permeable and impermeable stratigraphy. 32. A method as in claim 31, wherein said target stratum is directly overlain and capped by a capping layer of relatively low permeability. 33. A method as in claim 32, wherein said capping layer has a minimum thickness of about 1 meter, with a maximum permeability of approximately 10 miliDarcies. 34. A method as in claim 31, wherein said overburden includes within 100 meters above said target stratum a permeable zone having an average thickness of at least about 2 meters. 35. A method as in claim 14, wherein said target stratum is selected to lie generally horizontally, to have an average thickness of at least 5 meters, an average permeability of at least about 100 miliDarcies, a minimum porosity of about 15%, and a minimum compressibility of about 1.times.10 kPa. 36. A method as in claim 35, wherein said target stratum is further selected to have relatively little resistance to fracture propagation. 37. A method as in claim 14, wherein the following injection conditions are selected for use with a predominantly particulate waste streams: 38. A method as in claim 14, wherein the following injection conditions are selected for use with a slurry comprising predominantly viscous liquids: