Conversion Factors for Environmental Engineers978-1-59259-996-7/1.pdf · Conversion Factors for...
Transcript of Conversion Factors for Environmental Engineers978-1-59259-996-7/1.pdf · Conversion Factors for...
AppendixConversion Factors for Environmental Engineers
Lawrence K. Wang
CONTENTS
CONSTANTS AND CONVERSION FACTORS
BASIC AND SUPPLEMENTARY UNITS
DERIVED UNITS AND QUANTITIES
PHYSICAL CONSTANTS
PROPERTIES OF WATER
PERIODIC TABLE OF THE ELEMENTS
ABSTRACT
With the current trend toward metrication, the question of using a consistent systemof units has been a problem. Wherever possible, the authors of this Handbook ofEnvironmental Engineering series have used the British system (fps) along with themetric equivalent (mks, cgs, or SIU) or vice versa. For the convenience of the readersaround the world, this book provides a 55-page detailed Conversion Factors forEnvironmental Engineers. In addition, the basic and supplementary units, the derivedunits and quantities, important physical constants, the properties of water, and thePeriodic Table of the Elements, are also presented in this document.
Key Words: Conversion factors, British units, metric units, physical constants, waterproperties, periodic table of the elements, environmental engineers, Lenox Institute ofWater Technology.
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Index 811
Index
811
AAcid
-forming bacteria, 137phase, 137
Activated sludge, 10–22production, 10–13
Adsorber, 287Aerated static pile
bulking agents, 667energy requirements, 667–668environmental impact, 668–669oxygen supply, 666–667process, 664–670
description, 664Aerobic digestion, 177–205, 456–463
advantages, 178air requirement, 195autothermal thermophilic, 179–180
using oxygen, 181capital costs, 189–191continuous operation, 179design, 186–189
considerations, 181–185dewatering, 194–195mixing, 194oxygen requirements, 183–184pH reduction, 194solids reduction, 182–183temperature, 181–182
input–output data, 186–189parameters, 186–188performance
supernatant quality, 185–186volatile solids reduction, 185volatile solids loading, 194
design procedure, 186-189digester volume, 193-194, 196-197disadvantages, 178-179microbiology, 178O & M costs, 190–191oxygen requirement, 194–195, 196
performance, 185–186power requirement, 197process
description, 178–179variations, 179–181
semibatch operation, 179sludge
age, 196quantity, 193wasting schedule, 194
solids retention time, 194volatile solids reduction, 196
Agitated in-vessel composting bioreactor,671
Airand oxygen requirements, complete
combustion, 618compression, 265drying, 265filtration, 265preparation, ozone, 265saturation, flotation, 86-to-solids ratio, 81, 89, 90, 92, 93
Alkaline stabilization, 207advantages and disadvantages, 212biosolids
chemical characteristics, 220environmental impacts, 213deodorization, 217equipment, 216facility for biosolids, design factors,
216process performance, 217
chemical compounds in biosolids, 221,222
process design, 223lime handling facilities, 223
Anaerobicbiological reactions, 136contact
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812 Index
column schematic, 150process study procedures, 146schematic. 140
decomposition, 135digester
capital and operating costs, 162cost estimate, 162, 163covers, 150design examples, 163
using modified anaerobic contactprocess, 167
using standards design, 163performance criteria, 162
reactor configuration. 139external heat exchanger, 157gas
collection, storage, and distribution,158
piping schematic, 159utilization, 159
heating system, 154heat losses,156maintenance of reactor stability, 161mixing devices, 151sludge and supernatant withdrawal,
161sludge pumping and piping
considerations, 160system equipment and appurtenances,
150tank construction and system
components,149turbine-type mixing system, 155
digestion, 135, 457, 484, 487effect of solid detention time, 142effect of temperature, 142gas production and utilization, 142management, 160management, control of sludge feed,
160nutrient requirements, 142organic loading
parameters, 140rate, 141
reactor configurations, 138anaerobic contact process with
sludge recycle. 138anaerobic filter, 138single-stage, unmixed, 138two-stage, mixed primary. 138
solid waste, 135time and temperature relationships,
141wastewater sludges, 135
lagoons, 431, 432applications, 432application examples, 443construction cost, 440design criteria, 437design
examples, 443data gathering and compilation,
437energy
consumption, 440costs, 440
limitations, 432minimum top width, embankments,
439minimum treatment volume, 433operation and maintenance cost,
440process
design, 433performance, 432reliability, 432
sludge volume, 436volumes and depth requirement, 434waste volume for treatment period,
434volume requirement, 436with recycle system, 439
process, 136biochemistry, 137metabolic pathways, 139microbiology, 137recent development, 168performance data 171
reactor design and sizing, 146treatability studies, design practice, 144treatment process, 136
advantages, 136trickling filter, 140
Ancillary facilities, landfill, 724Animal wastes
anaerobic lagoons, 431treatment, 431
Annual evaporation data, 600Anoxic gas flotation, AGF, 492Ash, 357
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Index 813
ATAD, autothermal thermophilic aerobicdigester, 452, 456-463, 488
–air, 191–193, 452, 456, 460–oxygen, 191–193, 452, 456, 462–463
Attached-suspended growth biosolids,26–27
Average evaporation data in US, 438
BBacteria, 334–335Basket centrifuge, 103–104
achievable solids concentration, 103costs, 109–110
construction, 113O&M, 114
cycle time, 103energy requirements, 109–110feed rate, 103performance, 109–110, 118
Belt press, 255–258, 466Belt filter presses, 519–539
advantages, 521–522applications, 522cake thickness, 534capital cost, 530costs, 530–532design criteria, 523–527
pressures, 526–527disadvantages, 522energy requirements, 533-534O & M, 528–530
beltrate travel, 530tracking, 529
biosolids conditioning, 529compression, 530costs, 530-532inspection, 529loading rate, 530sampling and analysis, 529solids, 529spray adjustment, 529
odor control, 527-528performance, 522-523pressing capacity, 533pressures, 534principles, 520-–21weight of water in cake, 534
Biofiltration, 451, 453, 464, 466–470, 481applications, 468
costs, 469design considerations, 468process description, 467
Biologicalbiosolids, 10–27
characteristics, 10flotation, 72
Biosolidsand site conditions, 720anaerobic
digestion, 135anaerobic lagoon, 432
bacteria, 219centrifugation, 101–134, 466characteristics and quantity, 1–44characterization, 28–35, 717chlorine stabilization, 376–383class A, 707class B, 707codisposal with refuse, 716combustion, 614–618composting, 645–687
applicability, 647-649calculation of composting area
requirements, 681–682calculation of bulking agent to
biosolids ratio, 679calculation of the ratio of new to
recycled bulking agent, 679–681costs, 674–675
capital, 674–675design criteria, 654–659environmental impact, 647–649O & M, 675process description, 651–654
compressibility, 33–34conditioning cost, 364–368
capital, 364-365electricity means, 375O &M cost, 365-368
dewaterability, 29-31dewatering processes, 465digestion and stabilization, 454disposal on land (landfill), 712elutriation, 389evaporation, 583fixed solids, 34flotation, 71, 451heavy metals, 34–35high temperature thermal processes, 613
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814 Index
incineration, 620-627land application program, elements,
712landfill methods, 713
area fill layer, 715area fill mound, 715biosolis-only area fill, 714biosolids-only trench fill, 713dike containment, 715narrow trenches, 713wide trenches, 714
–lime mixing tankdesign, 228mixing, 230sizing, 229
low temperature thermal processes, 299management, 4oxyozosynthesis, 244pH, 34polymer conditioning, 389pressurized ozonation, 243production, 2, 737property, exceptional quality, 707septicity, 34sludge drying beds, 403slurries, mechanical mixer specifica-
tions, 231specific gravity, 28–29specific resistance, 33stabilization, 375–376
lime dose requirement, 214, 215storage with lime addition, pH change,
216temperature, 34thickening, 30-31, 71trace elements, 34–45vermicomposting, 689vertical shaft digestion, 451volatile solids, 34wasting methods, 20bridging model, destabilization of
colloids by polymers, 397Buchner funnel test, 362–364
CCapillary suction time (CST), 364
testing, 549–550Capital cost, codisposal by combustion,
starved air combustion (SAC),629
Carver–Greenfield dehydration system,591
Cationic polyelectrolyte in solution,configuration, 396
Cement kiln dust, 357Centrifugation, 101–134, 466
advantages, 124clarification and thickening, 101–134cannery waste sludge, 122coal and refuse, 114–121disadvantages, 124electroplating waste, 112–114metallurgical refinery sludge, 121–122paper sludges, 110–112potato wastes, 122principles, 102pulp sludges, 110-112
Centrifugesconstruction material, 124design, 122–126
applications, 128criteria, 125procedure, 125–126
effects of parameters, 125manufacturers, 123–124operation and maintenance, 126–128performance, 109–122selection, 122types, 103
Chemical biosolids, 27–28conditioning of, 354
Chemisorbed water, 102–103Chlorine, 272
stabilization, 376-383advantages, 379-380characteristics of stabilized biosolids,
380–381chlorine requirements, 379–380cost, 381–383disadvantages, 380process description, 376–378subnatant quality, 381supernatant quality, 381
Clarification, centrifugation, 101–134Class A biosolids, 209Class B biosolids, 209Classical pollutant removal
flotation, 256ozonation, 250, 289
Closed-loop ozonation, 288
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Index 815
Coal, 357Codisposal by combustion, 627
applications, 628design basis for costs, 629design parameters, 628energy requirements, 629environmental impact, 629performance, 628reliability, 628starved air combustion (SAC), 628
operating cost, 630Codisposal, biosolids/refuse mixture, 716Codisposal, biosolids/soil mixture, 716Coil spring-belt type vacuum filter, 500Colloidally bound water, 102–103Combustion, 614-–18
calculations, molal basis, 639chemical reactions, 616
Comparison, approximate and theoreticalcalculation, 641
Complete mix digester design, mean cellresidence times, 148
Completely mixed biological wastetreatment process, steady-staterelationships, 148
Composition of primary biosolids, 9–10Compost, 338, 464, 650–653
class A, 650class B, 650Exception Quality (EQ), 650metal concentration, 650processes
with external bulking agent, 658–659
without external bulking agent,656–658
quality, 649–651temperature, 650
Composted sludge, gamma irradiation, 345Composting, 338, 646
moisture, 651–653nutrient concentration, 653oxygen supply, 653pH, 653temperature, 653
Concurrent elutriation in multiple tanks, 393Conditioning
and stabilization, 353–388chemical, 359-364dosage, 357-358
Conduction drying, 306Continued leachate and gas control, landfill,
735Continuous
flow system, 695slaking, 228
Convection drying, 305Conventional digester, 138Cost
biosolids disposal on land (landfill), 735flotation, 86hauling of biosolids,738heat
conditioning, 303drying, 308
of recycling, land application, 712supplemental heat, lime addition and
electricity, 232sludge drying bed, 420VSD, 486, 488
Countercurrent elutriation, 390Cryogenic air separation, 285–286Cryophilic aerobic digestion, 192CT, concentration-time, 276Cyanide removal, ozonation, 291
DDAF (see also Dissolved air flotation)
concrete or steel construction, 76dissolved air flotation, 71, 251–255, 453hydraulic loading, 79, 82pollutants removal, 256rectangular or circular shape, 76, 78solids loading, 80thickener, 71–99, 463
design criteria, 73no recycle, 89, 91process description, 74process design, 88with recycle, 90, 93performance, 85
Decay coefficient, 14, 16, 17Deep-shaft bioreactor (VSB), 452Denitrification biosolids, 27Design criteria
for area fill layer, 716for area fill mound, 716for diked containment landfill, 716narrow trench landfill, 714wide trench landfill, 714
Wang_v6_Index_Final 7/23/07, 7:34 AM815
816 Index
Designparameters, hauling of biosolids, 736procedure, hauling of biosolids, 736
Diffuser contactor for water and waste-water treatment, 267–268
Digestergas holder cover, 152heat transfer coefficients, 156
Digestion, 451–489Dilution-to-threshold, D/T, 481Direct
drying, 305–indirect rotary dryer, 320–321
Disinfectionchemical, 336chlorine, 337electron irradiation, 339gamma irradiation, 343–349heat drying, 327high temperature thermal process,
338lime, 337long-term storage, 336low temperature thermal process, 337ozonation, 251, 276ozone, 274–276, 337quaternary ammonium compounds,
337solid substances, 336
Disk centrifuge, 107–108advantages, 108disadvantages, 108performance, 109
Dispersed air flotation, 71Dissolved air flotation (DAF), 71, 251–
255, 453double cell, 253single cell, 252
Dissolved gas flotation (DGF), 247–252DO, dissolved oxygen, 15Draft tube-type mixer, 154Dried sludge, gamma irradiation, 345Dry
feeders, 227powder cationic polyelectrolytes, 395solids heating values, effect on
autogenous combustion, 621solids heating values, effect on
supplemental fuel consumption,622
Dryingbeds, 403–430, 466lagoons, 585–590conduction, 306convection, 305
Dual digestion, 484, 485
EE. foetida, 691Earthworm
conversion process, process designconsiderations, 698criteria, 700limitations, 700operation, 699troubleshooting, 699
process diagram, 691Efficiencies, biosolids dewatering
processes, 737Electroflotation, 72Electron beam
facility, 340scanner, 341
Electron irradiation, 339–343design considerations, 341performance, 342process description, 340
Elutriation, 373, 36, 389chemical conditioning, soluble ionic
organic polymers(polyelectrolytes), 394
chemical conditioning, solublenonionic organic polymers,394
design examples, 399elutriate disposal considerations, 391process
benefit, 392design
considerations, 390new technology considerations,
391procedures, 392
reactor design considerations, 390Energy requirements, hauling of bio-
solids,738Environmental
control, landfill, 733, 734impact, DAF, 87problems, landfill, 734
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Index 817
Equipmentlandfill, 732performance characteristics, landfill,
729, 730selection and maintenance, landfill,
731Eudrilus eugeniae, 691Evaporation
data, USA, 600lagoons, 584–590process reactor, 584, 602
Evaporative efficiency, 313Evaporator, 590–604
applications and limitations, 592design considerations, 593heat transfer coefficients, 594multiple-effect, 596, 598process description, 590single-effect, 595solar, 603steam, 602triple-effect, 592vertical short-tube, 591
Examples, land application, 741Excess air
effect on supplemental fuel require-ment, 618
temperature, effect on supplementalfuel requirement, 618
Extended aerated piles, 666
FF/M ratio, 13, 17, 19Facility design, landfill, 722Factors affecting
biosolids conditioning, 354–356solids removal, 7–9the heat balance, 617that influence the production of WAS,
13–16FBF, fluidized furnace, 620–623Feed
composition, 15pattern, 16pump, 54
Ferric chloride, 356–357Fiber-cloth-belt type vacuum filter,
500Film layer purifying chamber contactor
for water, 266, 267
Filterleaf testing, 360–362media, 505–506process control
cake drying, 508chemical conditioning, 508efficiency, 508filter cake qualityheat treated biosolids, 508inspection, 509odor, 509optimum operation, 508production, 508-–09sampling and analysis, 509tank agitation, 508yield, 508
Filtration dewateringbasic theory, 495filter aids, 495–496pressure drop, 495 system, 495-497
Fixed digester cover, 151Fixed-volume recessed plate filter press,
542, 545Flash dryer system, 315Flash drying process, 316Flexibility, performance, and environ-
mental impacts, landfill, 728Float concentration, 82Floating digester cover, 152Flotation, 71–99, 251–255, 451, 462
cost, 86heavy metal removal, 256organic chemical removal, 256thickener, 462, 487
fluidized bed furnace, FBF, 620–623applications, 623design basis for cost, 624design criteria, 623energy requirements, 624environmental impact, 624operation data, 624performance, 623
Food pasteurization, 337Free water, 102–103Freeze–thaw, 373–374Fuel energy consumption rates,
construction equipment, 738Fungi, 336Furnace combustion, comparison,
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818 Index
approximate and theoreticalcalculation, 641
GGamma irradiation, 343–349
design considerations, 346dried or composted sludge, 345facility, 344labor requirements, 347–348operational considerations, 348power requirement, 345
Gas-phase biofiltration, 451, 453, 464,466–470, 481
GLUMRB Standards, 146Grading at completion of filling, landfill,
735Gravity thickeners, 47–55
advantages, 47, 48capital cost, 55compression and storage zone, 53cost, 55-56design, 56–61
considerations, 49input data, 57, 58output data, 61parameters, 58procedure, 59
floor slope, 54free board, 53hydraulic loading, 50maintenance materials cost, 56, 57minimum surface area, 49–51O & M cost, 55-57overflow rates, 52polymer addition, 54power consumption, 56settling zone, 53
HHauling of biosolids, 736
example, 741Heating values, sludges, 616High rate (mixed) digester, 141High temperature
operationsprinciples, 614
combustion factors, 614sludge fuel values, 614
processes, 613basic elements, 615
example, 619technology review, 620
thermal processes, 613advantages, 614
High-rate digestionsystems, 138VS reduction, 143
Hydrogen sulfide/sulfide equilibrium, pHeffect, 218
IIncineration
design example, 632of sludge FBF, 621
Inorganic polymer conditioning process,thickening and dewatering, 399
Input data, hauling of biosolids, 736
LLand application
advantages, 708of biosolids, 705
description, 706introduction, 705maximum metal concentrations,
708preliminary planning, 717
design criteria, 709disadvantages, 708performance, 710site suitability, 709
Landfillburial, lime stabilized biosolids, 211design criteria, 725equipment, 728method, selection, 719type and design, 724
Landfilling of screenings, grit, and ash,717
Landscaping, landfill, 735Leachate quality from biosolids only
landfill, 727Lime
addition, biosolids, dewatering andsettling characteristics, 219
bulk density, 227characteristics, 223, 224delivery and storage, 225feeding, 227-only and supplemental heating
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Index 819
pasteurization, 234capital and operating costs, 235cost comparison, 235
reactionhydrated lime, 225quick lime, 225
stabilization, 207current status and regulations, 208design, 237
component sizing, 237criteria, 213example, 235loading, 235, 236objective, 213
full-scale lime stabilization facility,208
history, 208of biosolids, applicability, 211operation, flow diagram, 210pathogen reduction, 218process description, 208systems
capital and operating costs, 232cost and energy usage, 232theory, 212
storage and feed equipment, 226Liquid
cationic polyelectrolytes, 396sludge vermistabilization (LSVS)
process, 692LSVS reactors, 692
MManagement and reporting, landfill, 731Maximum allowable pollutant concentra-
tions, biosolids, landfill, 723Mesophilic digestion, 141Methane
Fermentation Phase, 138formation
bacteria, 137step, 138
production equation, 144Minimum anaerobic digester capacities,
146Multiple
elutriation, 390in a single tank, 392hearth furnace
applications, 625
design basis for costs, 627design criteria, 626energy requirements, 626environmental impact, 626operations data, 627performance, 626
OObligate anaerobes, 137Operating schedule, landfill, 731Operation and maintenance
biosolids landfill, 728costs
area landfill, 740narrow and wide trench landfill,
739Operations plan, landfill, 731Organic wastes, nature, 136Output data, hauling of biosolids, 737Oxygen requirements, complete combustion,
617
PPart 503 Rule, 209, 707PFRP treatment, 231Pilot digester
schematic, 145study procedures, 145
Polyacrylamide molecule, 395Polyelectrolyte
additions for various sludges, 399conditioning process
dewatering, 398sludge thickening, 396
determination, 399process control, 399
Polymer conditioning, 389Process to Further Reduce Pathogens
(PFRP) Requirements, 694Progress in vermicomposting, outside US
696PSRP treatment, 230
RRaw sludge VS reduction, 143Recycling of biosolids, land application,
706Reduction in volatile matter by digestion,
141Regulations and standards, landfill, 722
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820 Index
SSAC, approximate combustion calcula-
tion, supplemental fuel require-ments, 637
Safety, landfill, 733Saprophytic bacteria, 137Sick digesters. 137Site and equipment costs
area landfill, 740narrow and wide trench landfill, 739
Site closure, landfill, 735Site selection methodology, landfill, 721Site selection, landfilling method, 719Sludge
heating system schematic, 155heating value, experimental methods,
616incineration
fluidized bed furnace, 623multiple hearth furnace (MHF), 624,
625regulatory matters, 642
moistureeffect on autogenous combustion,
621effect on supplemental fuel
consumption, 622washing (elutriation), 390
Standard rate (unmixed) digester, 141starved air combustion (SAC)
applications and limitations, 631approximate calculation method, 633capital cost, 633design basis for costs, 632design criteria, 632energy requirements, 632operating cost, 633performance, 631sludge, 629. 630theoretical calculation method, 638
Suitability of biosolids for landfill, 718
TThermophilic digestion, 141TPAD process, performance parameter,
173Two-stage anaerobic process, 137Typical biosolids application
rate scenario, example, 741scenarios, 711
Typical digester section, 149
UUltimate use, landfill, 735US EPA 40 CFR Part 503, 209, 707, 722
VVermicomposting process, 689
future development and direction,701
problems, 694process
application examples, 701description, 690
technologybreakthrough, 694development, 690
Vermiconversion System, 695Vermistabilization process
biosolids, 691current status, 697pioneers, 697resources, 697
Volatile solid loading factors, 147hydraulic detention time effect, 147sludge concentration effect, 147
Waste storage ponds, 441cross-section, 442layout, 442process description, 441process design, 441
Wastewater and sludge treatment, processselection, flow sheet, 391
Wang_v6_Index_Final 7/23/07, 7:34 AM820