Hazardous Wastes

  1. Defining "Hazardous Waste"
  2. RCRA
  3. CERCLA
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 

Defining "Hazardous Waste"  

I. Defining hazardous wastes is not as easy as you might expect!  All things are
   toxic if given in a high enough dose.  To put it another way, my favorite 
   chemistry professor at Stanford University, Dr. John Brauman, once said 
   "when humans don't understand something, they give it a name."  Hazardous 
   waste is a case in point, particularly in the minds of the public -- 
   the name itself conjures up fear and confusion. 
 
   Of course, one can hardly blame the public for their fear and confusion.  
   Consider, for example, a hypothetical molecule.  As this molecule travels 
   in different areas of the environment during its life cycle, it may be 
   given a baffling array of different names under different federal laws 
   as shown below (each term is in quotes). 
 
 
 
     during                  in the                    as a  
     production:             environment:              waste:
                                                             
                      |-->"hazardous air pollutants"-->|
                      |    [Clean Air Act (CAA)]       |
                      |                                |
    "toxic ---------->|-->"toxic pollutants"---------->|-->"hazardous 
     substances"      |    [Clean Water Act (CWA)]     |    wastes" 
     (TSCA)           |                                |    (RCRA)   
                      |-->"hazardous substances"------>|    
                      |    (CWA, RCRA, CERCLA)         |   
                      |                                |
                      |-->"hazardous materials"------->|
                           (HMTA)
 
We will define each of these laws in due time, but it's important to know for 
now that each law addresses the risk in different ways, and the final resting 
point is generally addressed by RCRA as a hazardous waste. 
 
 

II. Under RCRA (Resource Conservation and Recovery Act)

Hazardous waste is generally defined as "a solid waste that poses a substantial threat or potential danger to human health or the environment when improperly handled." However, this definition does not tell us what those threats or dangers are. Different wastes pose different risks, and they are not limited to toxicity. A starting point is to consider the different basic characteristics of hazardous wastes, as shown by the D-wastes below.

A. "D-Wastes" exhibit at least one of four characteristics:

1. ignitibility: flash point < 140 deg. F.

"Flash point" refers to ignition of a source to the point where a flash of light is released. It is not necessary a sustainable fire, but this definition acts as a standard for ignitibility. We heat up the waste to 140 deg. F. and place an ignition source next to it under prescribed laboratory conditions. If a flash occurs, it is defined as an ignitible waste. This waste is called a D-001 waste.

2. corrosivity: pH < 2, > 12.5

This waste is typically a very high or very low pH. An alternative definition is that this waste can corrode steel under specific laboratory conditions at a specified rate of greater than 1/4 inch per year. This waste is called a D-002 waste.

3. reactivity: explosiveness and toxic by-products from chemical reactions

These wastes may react violently with air, water, or other conditions (such as changes in pH or temperature), or these reactions may result in toxic by-products. This waste is called a D-003 waste.

4. toxicity: standard extraction procedure (EPA)

These wastes are determined by a standard extraction procedure developed by the EPA known as the toxicity characteristic leaching procedure (TCLP). A solution passes through the waste, and we measure concentrations in the extract. A rule of thumb is that if the concentrations are greater than 100 times the acceptable amount in drinking water, we have a toxic waste. These wastes are referred to as D-004 to D-043 wastes.

B. Four lists (defined and created by the EPA) that take precedence over the above characteristics:

The problem with the definition of D-wastes is that, by itself, it may encourage managers to dilute the wastes. For example, a hazardous waste might be made non-hazardous simply by diluting the waste (i.e., "the solution to pollution is dilution"). However, this is precisely what we DON'T want! Instead of spreading large amounts of these diluted wastes into our environment, it is more effective to encourage proper management of the waste while it is still concentrated For this reason, we use the following four lists. 

5. F-list: from generic processes, without regard to the type of industry producing the waste.

e.g., degreasing, solvents, and electroplating processes

6. K-list: from specific sources, listed by type of industry:

e.g., iron and steel industry, petroleum refining, pesticide industry, explosives

7. U-list: "toxic wastes" (subject to numerous qualifications).

Remember, the law does not allow these wastes to be diluted

8. P-list: "acutely hazardous"

e.g., highly explosive wastes, or wastes that are fatal at alow doses. These wastes present substantial hazards whether improperly managed or not (and therefore are subject to even tighter restrictions).

C. Mixtures of solid waste with waste listed above.

In other words, any attempt to dilute listed wastes with other solid wastes simply renders all the waste hazardous under the law. The definition is specifically designed to discourage dilution of wastes.

D. Waste from the treatment, storage, or disposal (TSD) of wastes listed above

In other words, even after treatment, storage, and disposal of a listed waste, there must be an accounting for these wastes.

Excluded wastes are excluded from RCRA, generally because they are addressed by other laws. Exampes of excluded wastes include:

  • domestic sewage,
  • onsite mining wastes
  • household wastes
  • agricultural wastes used as fertilizers
  • cement kiln dust.

Finally, there is a de-listing process, whereby a facility must prove to the EPA that their waste is different from the above categories and does not meet any of the criteria for a hazardous waste. In other words, the definition of a hazardous waste is a legal definition subject to challenge.

 


 
 

RCRA (and other acronyms) 

 
A. General Considerations 
 
Hazardous waste management (HWM) is replete with acronyms.  We start with 
basic acronyms fundamental to HWM.
 
DOT:       Department of Transportation                                    
 
HMTA:      Hazardous Materials Transportation Act,                 
           enforced by DOT (Department of Transportation).
 
HCS:       Hazard Communication Standard (OSHA)                            
           enforced by OSHA (Occupational Health and Safety Administration).
           This law requires the use of MSDS
           (Material Safety Data Sheets) in industrial uses.  
 
CHEMTREC:  CHEMical TRansportation Emergency Center (staffed by CMA)              
           (1-800-424-9300)      
           This number is only to be used in emergencies! 
                              
CMA:       Chemical Manufacturers Association   
                            
 
B. RCRA and HSWA                                 
The primary federal law for hazardous waste management is
RCRA (Resource Conservation and Recovery Act). 
Passed in 1976, the original law established federal authority 
(with EPA) for hazardous waste management.  RCRA was amended in 1984 by 
HSWA (Hazardous and Solid Waste Amendments).
As a starting point, there are 3 key areas to the law: 
 
1. Hazardous Waste Identification  
2. Transport of Hazardous Waste
3. Permitting of Hazardous Waste Facilities 
                     
This law also established 3 major tools in hazardous waste management: 
 
1. deadlines to control the delays of regulatory development.  
2. minimum regulatory controls that would be triggered 
   if EPA did not issue regulations.  Although these were statutes 
   (passed by Congress) they resembled regulations.  It reflected some 
   of the interesting conflicts of the Reagan era, and a congressional 
   strategy to override the rulemaking process.  
3. a national strategy for hazardous waste management in 
   the form of a waste management hierarchy.  The hierarchy is based on 
   the now familiar life cycle analysis that we have stressed throughout 
   the core series. In order of priority, the national strategy was:
                                                     
  • prevent generation of waste (i.e., source reduction)
  • minimize hazardous waste that is unavoidable
  • separate and concentrate wastes (for easier management)
  • reuse wastes
  • recycle or reclaim wastes
  • treat to reduce the hazard and volume
  • land disposal
The so-called "land-ban rules" stipulated that wastes must be treated 
before land disposal with BDAT (best demonstrated available technology).
 
      SQG:       small quantity generators (below legally 
                 prescribed quantities, generators are subject 
                 to less stringent RCRA requirements)    
 
 
 

CERCLA

RCRA does not address "uncontrolled sites" (abandoned or inactive sites).  
Therefore, in 1980, Congress passed CERCLA (Comprehensive Environmental 
Response, Compensation and Liability Act), also known as "Superfund."
The motivation for this law was simple enough: RCRA assumes properly 
operated facilities, but clearly there are a number of uncontrolled sites.  
Perhaps the most infamous example of this is Love Canal.
Over time, many people have regarded CERCLA as an "expensive failure."  
To be sure, the law has been expensive - it typically uses more resources 
than any other program in EPA.  However, failure is a little more 
difficult to define.  It depends on the three major issues addressed by 
the law:  response, compensation, and liability.
 
Response:     within the immediate time frame, there must be a 
               mechanism for rapid response.   
 
Compensation: Hazardous Substance Trust Fund 
              (the so-called Superfund) Originally, $1.6 billion 
              was allocated for cleanup of abandoned sites.  
              The funds came from from taxes on chemicals, corporations, 
              and general revenue. 
 
Liability:   Because of the tremendous damage than can come from abandoned 
              sites, CERCLA established stiff penalities for violators.  
              Any litigation in this area centers around a search for the 
              PRP (potentially responsible party).  
   8. RQ:        Reportable Quantity (under CERCLA, releases above 
                 this level must be reported to the national response 
                 center, a toll free hotline at 1-800-424-8802).   
 
                 For example, if the R.Q. for a hazardous waste
                 is 1 pound, then any release above 1 pound must
                 be reported.
 
   9. NCP:       National Contingency Plan  (the overall plan to 
                 identify and prioritize sites).                             
 
   10. CERCLIS:  Comprehensive Environmental Response, Compensation,         
                 and Liability Information System (an inventory,             
                 often a prelude to being placed on NPL)                     
 
   11. HRS:      Hazard Ranking System  (this is a system used to
                 rank superfund sites in order of highest to lowest
                 hazard).
                                  
   12. NPL:      National Priorities List (based on HRS) List 
                (this is the list of Superfund sites, 
                 currently more than 1000 sites)
                 
 
D. SARA
 
   13. ATSDR:   Agency for Toxic Substance and Disease Registry        
                A branch of the Public Health Service that
                investigates health effects at sites ("health assessments")
                and writes the toxicological profiles for chemicals at 
                Superfund sites.
 
   14. EPCRA:    Emergency Planning and Community Right to Know Act 
                 (title 3 of SARA)                                  
                 Also known as the "Bhopal law" because it was motivated
                 by the tragic release of methyl isocyanate in Bhopal India. 
     
   15. TPQ:      Threshold Planning Quantity (under SARA, 
                 releases above this level must be reported 
                 to the State Emergency Response Commission).
 
   16. TRI:      Toxic Release Inventory                            
 
 

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