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Solid/Haz Waste
CH 6 Solid and Hazardous Waste
Question | Answer |
---|---|
RCRA | Resource Conservation and Recovery Act |
CERCLA | Comprehensive Environmental Response, Compensation and Liability Act (Superfund) |
subtitle D | the solid waste probram (RCRA) |
subtitle C | the hazardous waste program (RCRA) |
subtitle I | the underground storage tank program (RCRA) |
MSW | municipal solid waste residences, commercial establishments and institutions |
MSW does not include | construction, demolition debris and auto scrap |
largest proportion of solid waste | paper and paper products |
hazardous waste | anything that is toxic, ignitable, corrosive and/or reactive |
infectious and radioactive waste | not presently regulated by RCRA |
source reduction | minnimize generation of waste at source (manufacturing, design or by reusing materials) |
P2 | pollution prevention |
pollution prevention | amount and toxicity of hazardous wastes are reduced |
examples of p2 | changing manufacturig processes, material substitution, changing equipment |
recycling | collectino reprocessing or remanufacturing materials for reuse |
resource recovery | recycling |
composting | uses natural biochemical decay processes to convert organic wastes into a soil conditioner |
aerobic composting | the quickest decomposition method and the least smelly- biological stabilizatino of organic wastes |
4 factors to control aerobic composting | 1. moisture (60%) 2. carbon:nitrogen ratio (30:1) 3. temperature (32-60c)4. oxygen (continuous) |
natural composting | parallel rows, moisturized and turned (large surface area) |
passive composting | uses pvc pipes, minimal cost, not much area, unskilled workers |
forced aeration | tubes of pvc pipes but blowers attached |
vermicomposting (worms used) | red wiggler (eisensia foetida) red worm (lumbricus rebellus) |
anaerobic fermentatin | biogas conversion to produce methane |
biogas byproducts | 60% CH4, 40%CO2traces of H2, N2, H2S |
rotary kiln incinerator | can handle solid and liquid |
grate type incinerator | large irregular shaped solid waste |
fluidized bed type incinerator | liquid, sludge or uniform size |
waste-to-energy | heat of combustion in form of electricity or steam |
mass burn facilities | unsegregated wastes feed furnace |
refuse derived fuel plants | noncombustibles removed first and the rest is shredded to produce fuel to be used in burners |
soil of choice in landfills | sandy loam |
trench method | level terrain, dirt is on top of buried material then compacted |
the area method | used on side of hill or slope- continues until slope is leveled |
valley or ravine method | refuse placed in a depressin and filled with dirt, compacted and built up then used for parks or golf courses |
TSD | treatment, storage and disposal (persuant to RCRA) |
TSD Requirements | Double liners, leachate collection systems, ground water monitoring |
deep well injection | pumps liquid wastes through lined wells into porous rock formations deep underground |
controlled incineration | burns at temps 750-3000F |
bioremediation | uses naturally occurring bacteria or fungi to degrade haz waste |
subsurface impoundments | hold haz wastes in liquid form and are open on surface |
subsurface impoundments must have | double liners and leachate collection systems and good ground water monitoring system |
waste piles | must comply with requirements for landfills and protect from wind dispersion |
haz waste landfills (requirements) | 2 or more liners, 2 leachate collection systems and ground water monitoring systems |
basic blocks of sanitary landfills | cells basic blocks of sanitary landfills waste is covered by how many inches of soil |
inspection | visit by EH , point not to uncover evidence |
oxygen concentration meter | range from 0-25% above 25% dangerous due to combustion |
combustible gas indicator | - measures percentag of the lower explosive limit (LEL) will alarm at 20% |
radiation survey | measures ionizing radiation >2 millirems/hour are Potent. Haz. |
colorimetric indicator tubes | uses color changes |
photoionization detector | air sample UV light and measures ionization |
flame ionization detector | hydrogen flame ionizes compound instead of UV |
risks assessments include (3) | hazard identification, dose response assessment, exposure assessment and risk characterization |
health assessment based on 3 things | environmental characterization, community health concerns, health outcome data |
ash residue | all the solid residue and liquids resulting from combustion of solid waste |
biodegradable material | waste that can be converted, usually by bacteria and microorganisms |
commercial waste | solid waste generated by stores, offices, restaurants, warehouses |
composting | controlled biological decomp of solid waste under aerobic conditions |
fly ash | residue from combustino of solid waste |
geomembrane | impermeable membrane used in landfills |
industrial waste | waste generated by manufacturing or industrial processes |
integrated solid waste management | source reduction, recycling, waste transformation, landfilling |
leachate | liquid resulting from precip percolating through landfills |
municipal solid waste | nonhazardous waste from households, non process related industry |
cost internalization | price items so that all steps, including disposal, are reflected |
combustion is great at | reduction- up to 9 fold |
special wastes | medical, animal, waste oil, old tires |
medical waste | any solid wastewhich is generated in diagnosis, treatment immunizatin, reearch or poduction of testing biologicals |
pre-treatment for landfilling medical waste | incineration or autoclaving |
windrow composting | windrows are 3-6 feet high, 6-15 feet wide, uncovered pads, frequent mixing. Odors will result if anaerobic |
in-vessel composting | enclosed container 1. plug flow 2. dynamic |
plug flow in-vessel | first in first out |
dynamic | agitated |
trench mothod | level ground or some slope, trenches are constructed and that material forms a ramp |
area or ramp method | flat or rolling to use the natural slope |
gases found in landfills | NH3, CO2, cO, H2, H2S, CH4, N2, O2 |
phase 1: initial adjustment | organic biodegradable components undergo bacterial decomp - aerobic cause air is trapped in |
phase 2: transition | oxygen is depleted and anaerobic conditions begin to develop |
phase 3: acid phase | organic acids increase and H2 decreases |
phase 4: methane fermentation | acetic acid and hydrogen gas produce methane and co2 the ph wil rise to more neutral 6.8 to 8 |
phase v: maturation | last portions of material is converted |
daily solid waste cover depth | 6" |
final landfill cover depth | 24" |
final fill slope | 4% |
depth of solid waste | 8-10 ft avg |
rdf fired combustor | refuse derived fuel (pellets or cubes) |
4 charactaristics of haz waste | 1. ignitability, corrosivity, reactivity, toxicity |
ignitability | fire hazard |
corrosivity | special containers required |
reactivity (explosiveness) | react vigorously or spontaneously with air, water or are unstable |
toxicity | may release toxicants to pose hazard |
RCRA haz waste does not include | domestic wastewater, irrigation or indust discharde under Water Pollution Control Act, nuclear materials, household wastes, mining and ag wastes less than 220lb/month |
RCRA of 76 expands purposes of | Solid Waste Disposal Act of 65 is expanded by |
RCRA amendments of 84 | double liner, leachate collection and no varianc from groundwater monitoring |
CERCLA of 80 | (superfund) regs leachate and haz substances from inactive haz waste sites |
TSCA of 76 | Toxic Substance Control Act regulates production use and disposal of chemicals |
the major generators of haz waste | primary metals, organic chemicals, electroplating, inorganics, textiles, petroleum, rubber and plastics |
location of transfer station | center |
garbage fed to hogs should be boiled for how many minutes? | 30 minutes |
baling, landfill equipment and pulping all achieve | volume reduction |
how much wast stream can be economically recovered?f | about half of the waste stream |
acidic conditions do what to methane producing bacteria | inhibit |
methane in air at what concentration explodes? | 5-15% |
temperature of second step of incineration | 1500-1800F |
landfill should be at least how many feet from a stream? | 200 feet |
describe final cover of landfill site | 24 inches of compacted soil, low permeability, graded to shed water |
leachate with high molecular weight organic compounds treated by | physicochemical methods like lime adition and settling |
leachate with low molecular weight organic compounds are best treated by | biological methods like activated sludge |
best sanitary land fill method for rolling terrain is | area or ramp method |
lift method uses what depth? | 8-10 feet |
dragline used at a landfill for: | digging trenches, stockpiling material and placing cover material |
operation of landfill should we (with or against prevailing wind) | with wind to prevent wind from blowing back into operator |
CHEMTREC | chemical emergency 24 hour advice |
thermal process in addition to incineration | cement kiln |
slope of lifts | 2:1 rise over run (1 rise and 2 runs) so 26.3 grade of 50% grade in a landfill cell |
gases produced at landfills | methane, carbon dioxide, hydrogen sulfice |
first 4-60 days of landfill | aerobic state |
after 60 days | anaerobic |
anaerobic byproducts | co2, h2s, ch4 |
F wastes | hazardous wastes from non-specific sources |
K wastes | haz wastes from specific sources |
P and U wastes | discarded commercial products, residues |
p wastes | acutely hazardous |
cradle to grave haz waste | generator of waste is responsible |
conditional exemption from RCRA | less than 100 kg of haz waste/month |
small quantity generators | less than 1,000 kg/month |
more than 100 kg haz waste during a month | 90 day storage limin begins |
CFR 40 | procedures for using haz waste manifest |
manifest | multicopy shipping form designed by EPA and DOT environmental justice |