![]()
Environmental
Health & Safety
July 2006
TABLE
OF CONTENTS
Section
Page
I. Introduction......................................................................................................................... 1
A. Purpose.......................................................................................................................... 1
B. Applicability................................................................................................................. 1
C. Regulatory Requirements.............................................................................................. 1
D. Clemson University's Classification.............................................................................. 2
II. Waste
Characterization........................................................................................................ 4
A. General........................................................................................................................... 4
B. Hazardous Waste Determination Procedures................................................................ 4
1. Solid Waste.............................................................................................................. 5
2. Hazardous and Miscellaneous
Regulated Wastes.................................................... 6
3. Empty Containers................................................................................................... 7
C. Hazardous Waste Minimization Requirements............................................................. 8
III. Hazardous
Waste Storage Procedures............................................................................... 21
A. General Procedures...................................................................................................... 21
B. Waste Storage Containers............................................................................................ 24
C. Labeling and Marking.................................................................................................. 24
D. Accumulation Time Limits.......................................................................................... 25
E. Inspections.................................................................................................................. 25
F. Record keeping and Reporting..................................................................................... 26
G. Training........................................................................................................................ 26
IV. Hazardous
Waste Pick-up Procedures.............................................................................. 34
A. General Procedures...................................................................................................... 34
B. Categorizing Hazardous Waste.................................................................................... 34
C. Preparing Hazardous Waste Removal Request........................................................... 35
D. Satellite Accumulation Area........................................................................................ 35
V.
Hazardous Waste Shipping Procedures........................................................................ 39
A. General Procedures...................................................................................................... 39
B. Labeling and Marking.................................................................................................. 39
C. Manifesting.................................................................................................................. 39
D. Land Disposal Restriction Certification...................................................................... 40
E. Placarding..................................................................................................................... 41
F. Record keeping and Reporting..................................................................................... 42
VI. Non-Routine
Activity Procedures..................................................................................... 43
A. New Waste Streams..................................................................................................... 43
B. Unlabeled Containers................................................................................................... 43
VII. Training
Requirements....................................................................................................... 46
A. Who Must be Trained and How Often....................................................................... 46
B. Scope of Mandatory Training Requirements.............................................................. 47
C. Training Required by Other Laws............................................................................... 47
D. Documentation and Training Records......................................................................... 48
Appendix A Hazardous Waste lists
Appendix B Hazardous Waste Incident
Standard Operating Procedures (evacuation plans not included but can be
obtained from EH&S @ 656-2583 or 656-1770)
Appendix C Hazardous Waste Management
Regulations (separate documents available from EH&S @ 656-2583 or 656-1770)
Appendix D Hazardous Waste Storage
Miscellaneous Information
LIST
OF FIGURES
Figure II-1 Logic
Diagram for Identifying Solid Wastes
Figure II-2 Exclusions
from the Definition of Solid Waste and Hazardous Waste
Figure II-3 Logic
Diagram for Determining When a Recycled Material is a Solid Waste
Figure II-4 Logic
Diagram for Identifying Hazardous Waste
Figure II-5 Logic
Diagram for Identifying if a Solid Waste is a Listed Hazardous Waste
Figure II-6 Logic
Diagram for Identifying if a Solid Waste Exhibits the Characteristic of
Ignitability
Figure II-7 Logic
Diagram for Identifying if a Solid Waste Exhibits the Characteristic of
Corrosivity
Figure II-8 Logic
Diagram for Identifying if a Solid Waste Exhibits the Characteristic of
Reactivity
Figure II-9 Logic
Diagram for Identifying if a Solid Waste Exhibits the Characteristic of
Toxicity
Figure II-10 Logic
Diagram for Identifying Miscellaneous Regulated Wastes
Figure III-1 Map
of Hazardous Waste Accumulation Areas (to be inserted by departments
as applicable)
Figure III-2 Hazardous
Waste Accumulation Building Location
Figure III-3 Hazardous
Waste Label
Figure III-4 Weekly
Hazardous Waste Inspection Form
Figure IV-1 Hazardous
Waste Removal - Department Checklist
Figure IV-2 Hazardous
Waste Removal Request
Figure VI-1 Sample
Out-for-Analysis Label
LIST OF TABLES
Table III-1 Environmental
Protection Agency Compatibility List
Hazardous Waste
Management Manual
I. INTRODUCTION
A. Purpose
This manual outlines the proper
procedures for managing hazardous waste at Clemson University, Clemson, South
Carolina. This document is
intended to serve as a "how-to" manual for Clemson employees, students
and subcontractors involved with the handling of hazardous waste. These procedures will be revised as
necessary to reflect changes in Clemson practices and environmental
regulations.
A description of hazardous
waste and hazardous waste determination practices is provided in Section II. A discussion of hazardous waste
minimization is also provided.
Hazardous waste storage
procedures are presented in Section III.
Section IV details the hazardous waste pick-up procedures. Section V provides off-site shipping
requirements for hazardous waste.
Procedures for addressing non-routine situations are detailed in Section
VI. Section VII outlines the
required training for applicable personnel.
B. Applicability
The procedures contained in
this hazardous waste management manual shall be followed by all Clemson
employees, students and subcontractor personnel employed by Clemson. The Environmental Compliance Officer
must approve any deviation from the procedures defined in this document in
writing.
C. Regulatory
Requirements
The Resource Conservation and
Recovery Act of 1976 (RCRA) requires generators of hazardous waste to comply
with the regulatory requirements contained in Title 40 of the Code of Federal
Regulations Part 262 (40 CFR Part 262).
This Part requires generators to ensure and fully document that the
hazardous waste they produce is properly identified, managed on-site for no
more than 90 days and transported to a RCRA-permitted treatment, storage or
disposal (TSD) facility. These
RCRA requirements are administered by the South Carolina Department of Health
and Environmental Control (SCDHEC) and implemented under the South Carolina
Hazardous Waste Management Regulations (R.61-79.262).
All procedures defined in this
manual are written for compliance with the above regulations.
D. Clemson
University's Classification
The South Carolina Hazardous
Waste Management Regulations apply to the storage, treatment, transportation
and disposal of wastes that either are listed by the Environmental Protection
Agency (EPA) or meet one or more of the characteristics of ignitability,
corrosivity, reactivity or toxicity as defined in 40 CFR 261.
Under these regulations,
Clemson University's main campus is currently classified as a "Large
Quantity Generator" of hazardous waste. Within this limitation, Clemson University personnel are
prohibited from:
á Treating a hazardous waste,
á Storing a hazardous waste at an accumulation point
for greater than ninety (90) days,
á Transporting hazardous waste away from the main
campus, and
á Negligent or otherwise unlawful waste disposal.
Clemson University provides its
departments with a single means for the lawful disposal of hazardous
waste. A state contract service is
maintained without charge to the generating department. Those within Clemson
University who have a potential for generating hazardous waste are responsible
for four primary management activities:
á Hazardous waste minimization
á Proper management of the waste material while it
is being generated
á Processing hazardous waste for removal.
á Obtaining the knowledge and putting that into
practice in the proper management of hazardous waste in accordance with all
federal and state regulations and laws
This manual defines the
procedures a department must implement in order to properly conduct these
activities. In order to simplify compliance with hazardous waste regulations,
each department may wish to select an EHS Departmental Coordinator for safety
and environmental compliance issues.
This individual will be trained by EHS in the appropriate regulations. A
fifth area of responsibility, Emergency Response Procedures for Accidental
Release of Hazardous Waste, is discussed in the Hazardous Waste Incident
Standard Operating Procedures (Appendix B).
CHEMICAL EXCHANGE BETWEEN
CLEMSON UNIVERSITY DEPARTMENTS IS ENCOURAGED UNDER THE SUPERVISION OF THE ENVIRONMENTAL COMPLIANCE
OFFICER.
SOME CHEMICALS ARE NOT
REGULATED AS HAZARDOUS SUBSTANCES BUT ARE, NONETHELESS, ENVIRONMENTALLY
UNFRIENDLY AND IT IS CLEMSON UNIVERSITY=S INTENT TO PROTECT THE ENVIRONMENT.
THE ENVIRONMENTAL COMPLIANCE
OFFICER WILL MAKE ALL FINAL DETERMINATIONS AS TO THE FINAL DISPOSITION OF ALL
CHEMICAL AND BIOLOGICAL SUBSTANCES THAT MAY BE HAZARDOUS.
II. WASTE CHARACTERIZATION
A. General
Any substance that no longer
serves its intended purpose and is destined for disposal should be evaluated by
the generator to determine if it meets the definition of a hazardous
waste. Every possible effort shall
be made by the department to identify each waste stream. Unknowns can be
accepted by the Environmental Compliance Officer conditionally, but may be
returned to the generating department for chemical analysis if the hazardous
waste contractor cannot categorize the waste through on-site tests. DO NOT GUESS AT THE IDENTITY
OR "CREATE" A NAME FOR AN UNKNOWN! A
wrongly identified waste, if released accidentally to the environment, if
exploding during disposal, or if causing the fouling of an incinerator
pollution control system, not only will harm life and property, but could
result in potential litigation.
Likewise, the indiscriminate discarding of unknown chemical substances
can have equally serious consequences.
NOTE: All radioactive waste, including those
radioactive wastes which meet the definition for a hazardous waste, must be
processed through Clemson University's program for radioactive waste disposal.
The following sources shall be
used to accurately characterize a waste stream:
á Section II of this Manual,
á Material Safety Data Sheets (MSDS),
á Process Knowledge.
In the event that a waste
chemical substance does not meet the regulatory definition of a RCRA hazardous
waste, yet the generator recognizes unique hazardous characteristics which are
not subject to other regulatory requirements, the generator shall contact the
Environmental Compliance Officer (656-1770 or 656-2583) to determine if the
waste substance should be disposed as a hazardous waste. Many hazardous
chemicals may not be RCRA regulated but may be regulated by other laws and
disposal restrictions.
B. Hazardous
Waste Determination Procedures
Waste material, which may be a
hazardous waste, is generated within three primary activities at Clemson
University. These activities
include:
á teaching
á research projects
á physical plant operations and maintenance.
The generators in these areas
are responsible for properly characterizing the waste generated to determine if
it is a hazardous waste. These
activities generate three general categories of hazardous waste:
á off‑specification chemical stock,
á research effluent and residue,
á facility operations and maintenance waste (e.g.,
paint related waste).
The waste characterization
process is defined in Figures II‑1 through II‑10. These flow charts guide the user
through a systematic decision‑making process for categorizing the
wastes. Note that a waste stream
may belong to more than one category; therefore, follow all of the
flow charts in order to properly characterize the waste. This process is discussed in more detail in the following
sections.
1. Solid Waste
The first question to be
answered when defining a waste stream is: "Is this material a solid
waste?" A solid waste is any
solid, semi‑solid, liquid or contained gaseous material that is discarded
or considered "inherently waste‑like" (R.61‑79.261.2). Materials, which are solid wastes, are
identified in Figure II‑1.
Several types of materials are
specifically excluded from the definition of solid waste under R.61‑79.261.4. These waste types are listed in Figure
II‑2. Some recycled
materials are also exempt from the definition of a solid waste. Some materials when recycled are solid
wastes and others are not; these materials are defined in Figure II‑3.
After reviewing Figures II-1,
II‑2 and II‑3 classify the waste stream as either a solid waste or
not a solid waste. If it is a
solid waste, proceed to Section II.B.2. and determine if the waste is also a
hazardous waste or if other regulatory programs (such as the Toxic Substances
Control Act (TSCA) regulate it. If
the material is not a solid waste, it may still be a miscellaneous regulated
waste; therefore, proceed to Section II.B.2.
2. Hazardous and Miscellaneous Regulated Wastes
In order for a waste material
to be a hazardous waste, it must first meet the definition of a solid waste
(Section II.B.1.). Figure II-4
outlines the procedure for determining which solid wastes are also hazardous
wastes. There are two different
ways a waste can be classified as a hazardous waste. It can be a listed hazardous waste and/or it can be a
characteristic hazardous waste. Figure II‑5, along with the tables in
R.61‑79.261.31 through 261.33, define listed hazardous wastes. If a waste is included in any of these
lists, and in the case of U and P listed wastes it is un-used, it is a listed
hazardous waste. These lists are
as follows:
á F‑listed waste from operations that are not
specific to a particular manufacturing operation (R.61‑79.261.31). Example: Spent halogenated solvents
used in degreasing.
á K‑listed waste from specific manufacturing
process (R.61‑79.261.32).
Example: Sludge from wood preserving.
á P‑listed acute hazardous commercial chemical
products (R.61‑ 79.261.33(e)).
á U‑listed toxic commercial chemical products
(R.61‑79.261.33(f)).
It is also necessary to determine
if a waste is a characteristic hazardous waste. The four hazardous waste characteristics are:
á ignitability,
á corrosivity,
á reactivity,
á toxicity
To determine if a solid waste
exhibits the characteristics of ignitability, follow Figure II‑6. Use Figure II‑7 to determine if
the waste exhibits the characteristics of corrosivity, and Figures II‑8
and II‑9 to determine if the waste exhibits the characteristics of
reactivity and toxicity, respectively.
If a waste exhibits any of the above four characteristics, it is a characteristic
hazardous waste. A waste may be
both a listed and a characteristic hazardous waste.
The generator of the waste must
also determine if it is regulated under TSCA or any other applicable federal or
state laws or regulations. A waste
does not necessarily have to be defined as a solid waste in order to belong in
these categories. Use Figure II‑10
to determine if the waste belongs in these additional waste categories.
3. Empty Containers
Residues of hazardous waste
remaining in a container may not be subject to the requirements specified in
this manual if the container meets the regulatory definition of an empty
container.
A container or an inner liner
removed from a container that has held a hazardous waste, except a compressed
gas or acute hazardous waste, is empty if:
á All wastes have been removed that can be removed
using common practices (e.g., pouring, pumping, aspirating), and
á No material pours out of the container when held
upside down or for Department of Transportation (DOT) recycling, no more than
2.5 cm (one inch) of residue remain on the bottom of the container or inner
liner, or
á No more than 3% by weight of the total capacity of
the container remains in the container or inner liner if the container is less
than or equal to 100 gallons, or
á No more than 0.3% by weight of the total capacity
of the container remains in the container or inner liner if the container is
greater than 100 gallons in size.
A container that has held a
hazardous waste that is a compressed gas is empty when the pressure in the
container approaches atmospheric pressure. However, it should be noted that releasing hazardous waste
from a compressed gas cylinder for the purpose of returning the cylinder to
atmospheric pressure is considered illegal discharge of a hazardous waste.
CAUTION! A container or an inner liner
removed from a container that has held a P-listed or acute hazardous waste (as identified in Appendix A)
is not considered empty until:
á The container or inner liner has been triple
rinsed using a solvent capable of removing the waste,
á The container or inner liner has been cleaned by
another method that has been shown in the scientific literature, or by tests
conducted by the generator, to achieve equivalent removal, or
á In the case of a container, the inner liner that
prevented contact of the acute hazardous waste with the container has been
removed.
The rinsate generated when
cleaning hazardous material from an acute hazardous waste containers, should be
managed in accordance with the requirements specified in this manual unless it
can be determined, using the procedures outlined in this section, that the
material is not a hazardous waste. NORMALLY, ALL RINSATE FROM ACUTE HAZARDOUS
WASTE CONTAINERS IS AN ACUTE HAZARDOUS WASTE AND SHOULD BE COLLECTED AND
MANAGED ACCORDINGLY.
á For disposal of empty containers into landfill at
Clemson University see Appendix D for guidance on defacing. Recycling should be
investigated.
C. Hazardous
Waste Minimization Requirements
EPA defines waste minimization
as the reduction, to the most feasible extent, of hazardous waste that is
subsequently treated, stored and disposed of. Waste minimization includes any source reduction or recycling
activity undertaken by a generator that results in either the reduction of the
total volume or quantity of hazardous waste, or the reduction of toxicity of
hazardous waste, or both, so long as the reduction is consistent with the goal
of minimizing the present and future threat to human health and the
environment.
The main ideas behind waste
minimization are toxicity, volume reduction and material substitution. Toxicity reduction means reducing the
degree of hazard associated with the raw material that, consequently, reduces
the degree of hazard of the waste.
Material substitution means the use of lesser or even nontoxic
materials.
The South Carolina Hazardous
Waste Management Regulations and the ever rising costs for disposal, dictate
that all possible efforts be taken to eliminate or reduce the generation of
hazardous waste. Clemson
University departments are responsible for assessing each source of hazardous
waste within their operations and for establishing control measures to ensure
that the least possible amount of waste is generated.
In anticipation of future
hazardous waste minimization audits by SCDHEC, each department should record
any efforts undertaken for hazardous waste reduction and submit the
documentation to the Environmental Compliance Officer on an annual basis. Waste reduction action is to be
implemented by an effective combination of the following methods:
á Non-hazardous reagents shall be substituted for
hazardous reagents where possible, to avoid generating hazardous waste.
á Current equipment that produces a hazardous waste
stream and can be replaced by a new technology that reduces or eliminates that
waste stream shall be given high priority in the selection and procurement of
replacement equipment.
á No greater quantity of a hazardous reagent shall
be procured than will be necessary to satisfy immediate planned usage. Unused chemical overstock constitutes a
large portion of hazardous waste generated at Clemson University.
á Any written agreement entered into by a department
with an industrial client, where hazardous reagents or samples are supplied for
specific research or experimental use on behalf of that client, shall include a
provision for return of the unused amounts to the client for appropriate
disposal.
á Any agent of a department shall not accept donations
of chemicals unless immediate planned usage is confirmed for the entire amount.
á Chemical reaction systems shall be preplanned and
designed so that by‑products and effluent may be rendered non-hazardous
in the process, prior to reaching waste status.
á Upon application of hazardous reagents such as
paints, pesticides, etc., the entire volume of material shall be applied or an
additional area shall be identified where any remaining excess can be properly
applied at the same rate, so that the entire amount can be depleted.
á Upon termination of an employee or separation of a
student, the exit process shall include immediate collection of all chemical
reagents and waste residues used by or in the possession of that person. Prior
to separation, the department is responsible for documenting the identity of
each chemical reagent collected.
The intent here is to ensure
that unused chemicals are returned to the department chemical stores and placed
on inventory for continued use, wherever possible. Also, this procedure can help prevent the need for future
analysis of "unknown" chemicals.
Until an effective chemical
stock management program is introduced throughout Clemson University, old
chemical stock will be a major portion of the waste stream. Some of this old stock is hazardous
waste. Other constituents of this
old stock may not meet the definition of hazardous waste. However, these wastes usually cannot be
accepted into local sanitary or solid waste landfills. In order that liabilities are minimized,
these chemical wastes are given to a hazardous waste disposer and classified
managed as non-RCRA regulated wastes. From a regulatory standpoint, these
unused chemicals are not hazardous wastes. From a cost standpoint, disposal of these chemicals as wastes
may cost as much as the disposal of hazardous waste.
When a department generates
chemical wastes, old stock chemicals may not meet the hazardous waste criteria
and should be separated from those determined to be hazardous waste. The hazardous wastes shall be fully
managed as regulatory requirements dictate. The other chemical wastes should be managed in a practical
way and recycled if possible. When
pressed further by waste minimization requirements, Clemson University may
examine other options for dealing with these other chemical wastes.
Figure
II-1
Logic Diagram for
Identifying Solid Wastes
Figure
II-2
Exclusions from the
Definition of
Solid Waste and Hazardous
Waste
Figure II-3
Logic Diagram for
Determining When a
Recycled Material is a Solid
Waste
Figure II-4
Logic Diagram for
Identifying Hazardous Wastes
Figure
II-5
Logic Diagram for
Determining if a
Solid Waste is a Listed
Hazardous Waste
Figure
II-6
Logic Diagram for
Determining if a Solid Waste
Exhibits the Characteristics
of Ignitability
Figure
II-7
Logic Diagram for
Determining if a Solid Waste
Exhibits the Characteristics
of Corrosivity
Figure
II-8
Logic Diagram or Determining
if a Solid Waste
Exhibits the Characteristic
of Reactivity
Figure II-9
Logic Diagram for
Determining if a Solid Waste
Exhibits the Characteristic
of Toxicity
Figure II-10
Logic Diagram for
Identifying
Miscellaneous Regulated
Wastes
III. HAZARDOUS WASTE STORAGE PROCEDURES
A. General
Procedures
Two types of hazardous waste
accumulation points are present at Clemson University's main campus:
á Accumulation Points
á Satellite Accumulation Points
A hazardous waste
accumulation point is a location on-site at which hazardous waste can be accumulated for
up to 90 days without a permit. At
an accumulation point, any amount of hazardous waste can be collected and
stored providing no container remains in the accumulation point storage for
over 90 days. If hazardous waste
is added to a container at the accumulation point, the 90-day limit for that
container begins as soon as the first waste is added to the container. For this
reason, container size selection is very important in minimizing costs when
accumulating in these areas. Estimate your waste volume carefully while
allowing for extra time to arrange shipping. It is recommended that you chose a container size that you
can fill within a 30 or 60-day period in this situation.
A satellite accumulation
point is a
location at or near the point of generation that is under the control of
the operator of the process generating the waste. No more than 55 gallons of hazardous waste or one quart of
acute hazardous waste can be accumulated at a satellite accumulation point.
The difference between a
satellite accumulation point and an accumulation point are the volume and the length of
time wastes may be accumulated. At
a satellite accumulation point, up to 55 gallons of hazardous waste or up to
one quart of acute hazardous waste may be accumulated for a reasonable amount
of time. At an accumulation point, an unlimited volume of waste may be
accumulated in containers for up to 90 days. If a facility has not been approved by the Environmental
Compliance Officer to maintain a hazardous waste accumulation point, then they
are, by default, satellite accumulation points and must stay in status with the
volumes stated above.
The location of any
Departmental Accumulation Points will be inserted as necessary in Figure
III-1. The location of the Central
Hazardous Waste Accumulation Building is depicted in Figure III‑2. No hazardous waste shall be stored at
an Accumulation Point at Clemson University's main campus for greater than 90
days from the accumulation date on the container.
Hazardous waste must be kept in
designated areas at all times. Wastes that are accumulated in these areas must
be managed in accordance with the procedures specified below. The generator is responsible for
ensuring compliance with these procedures for his/her hazardous waste satellite
accumulation point(s). The
Environmental Compliance Officer is responsible for managing the Central
Hazardous Waste Accumulation Building(s) in compliance with these procedures.
All hazardous waste
Accumulation Points must meet the following requirements:
á A Hazardous Waste sign must be posted at each
area.
á The name and phone number of the accumulation
point supervisor and an alternate contact must be posted at each area.
á The area should be used for hazardous waste
accumulation only. No raw materials or chemical stock should be stored
in the same area with hazardous waste.
á Flammable materials cabinet shall be used when
possible for storage of ignitable hazardous wastes.
á The area must be located at or near the point of
waste generation and must be under the control of the person responsible for
the waste‑generating process.
á All containers will be appropriately labeled and
segregated for compatibility.
Access to the hazardous waste
accumulation points and building must never be blocked. The area shall be quickly and easily
accessible by emergency response personnel in the event of a spill, leak or
fire. Appropriate emergency
response equipment shall be maintained for each hazardous waste accumulation
and satellite area. The accumulation
point supervisor is responsible for ensuring the equipment is in good condition
at each of his/her accumulation points. The Environmental Compliance Officer is
responsible for the Central Hazardous Waste Accumulation Building(s). Emergency equipment shall include the
following:
á Fire extinguisher, 20lb ABC type.
á Absorbent of the proper type and of sufficient
amount to absorb the volume present.
á Broom, bucket and mop.
á Telephone or other communication device.
á First aid kit.
á Safety shower and eye wash station as applicable.
á Coveralls, eye protection and gloves compatible
with wastes.
á Empty containers and bags compatible with cleanup
characteristics.
The accumulation point shall be managed as follows:
á The person responsible for the area must meet the
Occupational Safety and Health Administration (OSHA) requirements for hazardous
waste training contained in 29 CFR 1910.120 and Department of Transportation
(DOT) HM-181/ HM-126F.
á Waste shall be stored in approved containers.
á Containers shall be kept closed except during
waste transfers.
á Inspections shall be conducted weekly (see
Section III.E).
á Incompatible materials shall not be combined
into one container. Containers of incompatible materials shall be separated to
protect against mixture in the event of a spill, leak or release (see EPA
compatibility table - Table III-1).
á Containers shall be labeled with an approved
hazardous waste label before any waste is received (see Section III.B).
Satellite accumulation
points are subject
to the following requirements defined below:
á No more than 55 gallons total of hazardous waste
or one quart total of acute hazardous waste may be accumulated. See Appendix A
for a list of acute hazardous wastes.
á Containers
with the excess must be dated as soon as 55 gallons of hazardous waste or
one-quart total of acute hazardous waste or more are accumulated. All
subsequent containers will be dated upon initiation of the first addition of
waste until the site's status is returned to a Satellite Accumulation point by
the reduction of wastes at the site to meet the less than 55 gallons of
hazardous or less than one quart of acutely toxic waste limit. This should be
accomplished within 3 days. In
order to minimize the establishment of new Accumulation Points, containers must
be moved to an established or central accumulation point within three days of
the date the storage volume limits are exceeded, unless permission to establish
a new Accumulation Point is obtained from the Environmental Compliance Officer.
In order to minimize the risk
of hazardous waste incidents and in order to comply with published regulations,
each site of hazardous waste generation will be considered a satellite
accumulation point unless designated otherwise by the Environmental Compliance
Officer. This will be particularly useful considering the large number of
laboratories generating hazardous waste on campus.
In spite of the flexibility
allowed in the regulations concerning volume limits at satellite accumulation
points, it will be Clemson University's procedure to pick up hazardous waste on
demand. This will also minimize
the risk of potential hazardous waste incidents by not allowing undue accumulation
of waste.
B. Waste
Storage Containers
Hazardous waste shall be placed
only in approved hazardous waste containers. An approved hazardous waste container is made of or lined
with a material compatible with the waste. Empty containers, which originally held the primary waste
constituent or similar material, are acceptable hazardous waste
containers. The original container
label must be removed or defaced.
An approved hazardous waste label with the appropriate information shall
be affixed to the container before any hazardous waste is received. (Container labeling requirements are
summarized in Section III.C)
The container must be in good
condition without holes, rust or dents.
The container shall always be closed during storage, except when waste
is being added or removed. A
hazardous waste container shall not be opened, handled or stored in a manner
that may rupture the container or cause it to leak. Consideration should be
given to doubly contain certain particularly dangerous chemicals if storage
conditions and limitations are not ideal.
If drums are stacked in the
Hazardous Waste Accumulation Building, pallets shall be used to separate the
containers, and stacking and spacing shall meet applicable fire protection
requirements. Aisle spacing for
container storage in the Hazardous Waste Accumulation Building shall be such
that each row of containers can be easily inspected for leakage or damage.
C. Labeling
and Marking
An approved hazardous waste
label (Figure III-3) shall be affixed to each hazardous waste container prior
to receiving any waste material.
The Environmental Compliance Officer is responsible for ensuring each
container is properly labeled before being picked up from a Satellite
Accumulation Point or an Accumulation Point and moved to the Central
Accumulation Point. However, the
Generator or Accumulation Point Supervisor responsible for the waste is
responsible for ensuring each container in his/her area is properly labeled
before placing waste into the container or receiving any waste into an
Accumulation Point.
The following information shall
be provided on each hazardous waste label:
á HAZARDOUS WASTE ‑ Federal law prohibit
improper disposal. If found,
contact the nearest police or public safety authority or the U.S. Environmental
Protection Agency.
á The specific chemical name of the hazardous waste
in the container shall be identified (e.g., waste acetone), including
percentages of constituents if more than one.
á Each container shall be appropriately labeled with EPA
Hazardous Waste Number
The labels shall be placed on
the side of each container in such a manner that they are clearly visible for
inspection.
Up to 55 gallons total of
hazardous waste or one quart total of acutely hazardous waste may be collected
in each satellite area. The
accumulation point supervisor is responsible for notifying the Environmental
Compliance Officer as soon as 55 gallons of hazardous waste or one quart of
acutely hazardous waste have been collected (see Section IV). Each container that is stored in the
Central Hazardous Waste Accumulation Building or other at any other
Accumulation Points shall have the accumulation start date on the label.
D. Accumulation
Time Limits
Up to 55 gallons total of
hazardous waste or one quart total of acutely hazardous waste may be collected
in each Satellite Accumulation area.
Once 55 gallons of hazardous waste or one quart of acutely hazardous
waste has accumulated, the Generator shall date the container(s) containing the
excess waste. The container(s)
must be moved to a designated university Accumulation Point or picked up for
off‑site disposal within three (3) days of declaration to the
Environmental Compliance Officer.
Within 90 days of the accumulation start date, the container must be
shipped off-site for disposal at an approved RCRA disposal facility. Hazardous waste may not be stored on‑site
at a designated Accumulation Point for greater than 90 days from the date it is first
accumulated.
E. Inspections
The applicable accumulation
point supervisor shall conduct weekly inspections of the hazardous waste
accumulation points and a copy kept on file at the site. The Environmental Compliance Officer or
his/her qualified designee shall inspect the Central Hazardous Waste
Accumulation Building(s). During
the inspection, the inspector shall check each item listed on Figure III‑4. The results of the inspection shall be
documented on this form. A copy of
the form shall be sent to the Director of Environmental Health and Safety and
one copy retained on site for inspection.
If any corrective action is
required, the Accumulation Point Supervisor must comply immediately. Once the problem has been corrected,
the Accumulation Point Supervisor is to date and initial a copy of the form and
mail it to the Environmental Compliance Officer. The Environmental Compliance Officer shall maintain these
records for three years.
F. Record keeping and reporting
During the weekly inspections
of the departmental accumulation points and the Central Hazardous Waste
Accumulation Building(s), the current inventory of waste shall be recorded (see
Section IV). The Environmental
Compliance Officer, for the purpose of coordinating shipments of hazardous
waste, shall use this inventory.
Within 30 days after the end of
each calendar quarter, a written report must be submitted by the Environmental
Compliance Officer to SCDHEC summarizing the hazardous waste activities for
that quarter. In addition to
general facility information, the report must include the following
information:
á Hazardous waste transporters used during the quarter to
transport the waste to a treatment or disposal facility.
á The types and quantities of hazardous wastes generated,
including the EPA waste number and the DOT hazard class.
á The types and quantities of wastes shipped off site during
the quarter.
á The types and quantities of waste remaining in storage
at the end of the quarter.
á A description of waste minimization and toxicity
reduction efforts for the year (to be included with the fourth quarter report).
And
á A description of the effectiveness of the waste
minimization and toxicity reduction efforts using comparisons to previous years
(to be included with the fourth quarter report).
All quarterly reports must be
maintained at the facility for at least three years from the date the report
was filed.
G. Training
Personnel who handle or are
occupationally exposed to hazardous waste are required to be trained initially
in the proper methods for the management of hazardous waste and the
implementation of the facility's contingency plan. The training program must be directed by a person trained in
hazardous waste management.
Personnel who are assigned to a position related to hazardous waste management
must complete training within six months of their assignment. These personnel must not work in
unsupervised positions until they have successfully completed training. Refer to Section VII for details
regarding who must be trained and the scope of the required training.
Table
III-1. Environmental Protection
Agency (EPA) Compatibility Table.
EPA has published a list of
potentially incompatible wastes, waste components and materials along with the
harmful consequences of mixing those materials together. This list does not include every
possible hazardous chemical reaction, but should be used as a guide in
packaging and storing these materials.
The list indicates the potential consequences of the mixing of a Group A
material with a Group B material.
For example, mixing any Group
2-A waste, which include reactive metals and metal hydrides, with a Group 2-B
waste, which include the Group 1-A alkaline and the Group 1-B acidic wastes,
may produce a fire or explosion and the generation of flammable hydrogen
gas. Mixing a Group 3-A waste, which
includes alcoholÕs and water, with a Group 3-B waste, which encompass Groups
1-A, 1-B and Group 3-B listed chemicals, may produce a fire, explosion or heat
and the generation of flammable or toxic gases.
These compatibility listings
and packaging guides should not be the only information used when packaging or
accumulating waste chemicals. RCRA
regulations require that wastes should be adequately analyzed by TSD facilities
so uncontrolled substances or reactions do not occur. Pay close attention to any waste characterization data you
receive on material reactivity and compatibility. There are also other sources of data that may be helpful in
determining waste compatibility.
MSDSÕs contain a section devoted to chemical reactivity and
incompatibility. The National Fire
Protection Association (NFPA) publishes a manual of hazardous chemical
reactions which contains over 3,500 documented dangerous chemical reactions.
Group 1-A
Acetylene sludge
Alkaline caustic liquids
Alkaline cleaner
Alkaline corrosive liquids
Alkaline corrosive battery fluids
Caustic wastewater
Lime sludge and other corrosive alkalies
Lime wastewater
Lime and water
Spent caustic
Group 1-B
Acid sludge
Acid and water
Battery acid
Chemical cleaners
Electrolyte, acid
Etching acid liquid or solvent
Pickling liquor and other corrosive acids
Spent acid
Spent mixed acid
Spent sulphuric acid
Potential consequences: Heat
generation; violent reaction.
Table
III-1. EPA Compatibility Table
(continued)
Group 2-A
Aluminum
Beryllium
Calcium
Lithium
Magnesium
Potassium
Sodium
Zinc powder
Other reactive metals and metal hydrides
Group 2-B
Any waste in Group 1-A or 1-B
Potential consequences: Fire or
explosion; generation of flammable hydrogen gas.
Group 3-A
AlcoholÕs
Water
Group 3-B
Any concentrated waste in Groups 1-A or 1-B
Calcium
Lithium
Metal Hydrides
Potassium
SO2Cl2, SOCl2,
PCl3, CH2SiCl2
Other water-reactive waste
Potential consequences: Fire,
explosion, or heat generation; generation of flammable or toxic gases.
Group 4-A
AlcoholÕs
Aldehydes
Halogenated hydrocarbons
Nitrated hydrocarbons
Unsaturated hydrocarbons
Other reactive organic compounds and solvents
Group 4-B
Concentrated Group 1-A or 1-B
wastes
Group 2-A wastes
Potential consequences: Fire,
explosion or violent reaction.
Table
III-1. EPA Compatibility Table
(continued)
Group 5-A
Spent cyanide and sulfide
solutions
Group 5-B
Group 1-B wastes
Potential consequences: Generation
of toxic hydrogen cyanide or hydrogen sulfide gas.
Group 6-A
Chlorates
Chlorine
Chlorites
Chromic acid
Hypochlorites
Nitrates
Nitric acid, fuming
Perchlorates
Permanganates
Peroxides
Other strong oxidizers
Group 6-B
Acetic acid and other organic
acids
Concentrated mineral acids
Group 2-A wastes
Group 4-A wastes
Other flammable and combustible wastes
Potential consequences: Fire,
explosion, or violent reaction.
Source: 40 CFR 264, Appendix V.
Figure III-1
Map of Hazardous Waste
Accumulation Points
(to be inserted by
department)
Figure
III-2
Figure
III-3
Figure
III-4
IV. HAZARDOUS WASTE PICK‑UP
PROCEDURES
A. General
Procedures
When requesting a hazardous
waste pick‑up the generator shall:
á Verify that a correct hazardous waste
determination has been conducted.
á Complete a Hazardous Waste Removal ‑
Department Checklist (Figure IV‑1).
á Complete a Hazardous Waste Removal Request form
(Figure IV‑2) and submit it to the Environmental Compliance Officer with
a copy of the completed Department Checklist.
á Follow up with the Environmental Compliance
Officer to ensure that the hazardous waste is removed from a satellite area
within three days of the accumulation start date and that no waste is
accumulated on site for greater than 90 days from the date it is generated.
The generator must initiate a
request for a hazardous waste pick-up. Usually when the total accumulated
volume of waste in the satellite area approaches 55 gallons of hazardous waste
or one quart of acutely hazardous waste. All accumulated waste must be removed
from the satellite area within three days of reaching these volume limits. However, it will be Clemson
University's procedure to pick up waste immediately after generation and upon
demand.
NO HAZARDOUS WASTE SHALL BE
DISCARDED IN GENERAL REFUSE, THROUGH WASTEWATER DRAINS, BY BURNING, BURIAL,
SALE, GIVEAWAY, OR ANY ROUTE OTHER THAN THAT PROVIDED BY CONTRACT WASTE
DISPOSAL SERVICE THROUGH THE ENVIRONMENTAL COMPLIANCE OFFICER.
CHEMICAL EXCHANGE BETWEEN
UNIVERSITY DEPARTMENTS IS ENCOURAGED UNDER THE SUPERVISION OF THE ENVIRONMENTAL COMPLIANCE
OFFICER.
B. Categorizing
Hazardous Waste
The generator shall assign an
EPA hazardous waste code to each waste stream upon generation. The following hazard codes shall be
used to indicate the class or type of waste:
Ignitable
Waste D001-
see Figure II-6 (and check the F-list)
Corrosive Waste D002-
see Figure II-7
Reactive Waste D003-
see Figure II-8
Toxicity Characteristic Waste See
Figure II-9 (D-List)
Acute
Hazardous Waste See
appendix A the P-List (also check F-List)
Toxic Waste See
appendix A the U-List
Non
RCRA regulated NR
(all waste hazardous materials not falling under an above category but destined
for disposal or recycling)
Ignitable, corrosive, reactive
and toxicity characteristic wastes are those hazardous wastes identified by the
characteristics outlined in 40 CFR 261 Subpart C. The hazardous wasteÒlistsÓ are found in 40 CFR 261.31, .32
and .33
C. Preparing
Hazardous Waste Removal Request
The generator to request a
hazardous waste pick-up shall follow the following procedures:
á Complete a Hazardous Waste Removal Request form.
á Obtain signature of the Department Head.
á Submit completed form to the Environmental
Compliance Officer.
á Append one copy to the Department Checklist and
attach paperwork to the associated hazard waste.
D. Satellite
Accumulation Point
Hazardous waste shall be
accumulated safely by the department until removed by the Environmental
Compliance Officer or contract hazardous waste service representative. Removal will take place as soon as
possible after notification is given to the Environmental Compliance Officer
but no later than within three days of the accumulation start date for excess
wastes.
Ignitable wastes shall be
stored in accordance with fire safety requirements for storage of
flammables. Contact the University
Fire Department for information (656‑2323).
Corrosive wastes shall be
stored in accordance with procedures for storage of corrosive materials, with
secondary containment employed to prevent contamination or reaction from
leakage.
Poisonous wastes shall be stored
in exhaust‑ventilated areas and double contained to prevent leakage.
Reactive wastes shall be
isolated and reported to the Environmental Compliance Officer for immediate
removal or special handling by the contract hazardous waste service
representative.
Specific storage procedures
referenced above may be found in "Prudent Practices for Handling
Hazardous Chemicals in Laboratories". A
copy of this book, cited in 29 CFR 1910.1450, OSHA's laboratory standard for
occupational exposure to hazardous chemicals in laboratories, is kept at the
office of Environmental Health & Safety.
Figure
IV-1
HAZARDOUS
WASTE REMOVAL - DEPARTMENT CHECKLIST
(1) _____ Each potential waste substance is identified and its container
marked with the container contents.
(2) _____ The generator of the waste has confirmed that no further
possible use of the substance exists within the department or in other Clemson
University departments.
(3) _____ The waste is a hazardous waste according to the South Carolina
Hazardous Waste Management Regulations or after consultation with the
Environmental Compliance Officer is declared hazardous.
(4) _____ The waste is not radioactive and does not contain PCBs.
(5) _____ The waste has been screened and categorized according to
hazard type.
(6) _____ A label with the words Òhazardous wasteÓ (see Òlabeling and
markingÓ, pg. 39 for exact verbiage required) has been affixed to each
container, complete with the chemical name(s) and waste code(s).
(7) _____ A Hazardous Waste Removal Request form (Figure IV-2) has been
prepared for each existing hazard category.
(8) _____ Each request has been copied. One copy for department records
directed through the Faculty member responsible and/or Department Head, and the
remaining copy has been affixed to the waste group while awaiting pick-up.
(9) _____ Each group of hazardous waste is being temporarily stored in
accordance with safety requirements for that specific hazard category.
Figure
IV-2
V. HAZARDOUS WASTE SHIPPING
PROCEDURES
A. General Procedures
Pre‑transport regulations
are designed to provide safe transportation of a hazardous waste from origin to
ultimate disposal. The pre‑transport
regulations used by the Department of Transportation (DOT) for transporting
hazardous waste (49 CFR 172, 173, 178, and 179) were adopted by the South
Carolina Public Service Commission and are referenced in R.6179.262. These pre‑transport regulations
apply only to hazardous waste shipped off site.
B. Labeling and Marking
An approved hazardous waste label
(Figure III‑3) shall be affixed to each hazardous waste container prior
to off‑site shipment.
Labeling requirements and marking regulations are found in R.61‑79.262
and 49 CFR 172.101, Hazard Material Table. These regulations specify the
following:
á containers must be labeled in accordance with the DOT
Hazardous Materials Table (available from the Environmental Compliance
Officer); and
á containers must be marked with the following
information:
‑ Proper chemical name
‑ Percent of constituents
if applicable
- EPA waste codes
- University Tracking I.D.
number
-
Accumulation Date
The Environmental Compliance
Officer is responsible for ensuring this information is provided prior to off‑site
shipment.
C. Manifesting
When hazardous waste is shipped
off-site for treatment or disposal, it must be accompanied by a properly
completed and signed Hazardous Waste Manifest. This form has multiple copies for distribution as
described in this section. The
facility to which the waste will be shipped will provide a copy of the blank
manifest to Clemson University.
Blank manifests may also be obtained from SCDHEC. Emergency response
information for each waste shipped must accompany all manifest.
The Hazardous Waste Manifest
must be completed by Clemson University before offering any hazardous wastes
for shipment. To facilitate record
keeping, the manifests are numbered in sequential order and no numbers are
skipped.
The information listed in Item
11 of the Hazardous Waste Manifest (US DOT Description) must comply with DOT
requirements (49 CFR 172.101) for proper shipping name, hazard class and
identification number.
The quantity is to be specified
by a whole number only (Item 13) and includes the entire container. The units for this quantity (Item 14)
must also conform to DOT standards.
The EPA waste code number for
each waste listed in Item 11 must be identified in Item I.
As a generator of hazardous
waste, Clemson University is responsible for initiating the manifest with each
shipment of waste. The generator
completes the sections of the manifest outlined above and signs and dates the
appropriate section of the manifest.
At the time the waste is picked up, the transporter signs and dates the
manifest in the appropriate section indicating that he has accepted the waste
and agrees to deliver it to the designated treatment, storage or disposal
facility.
The generator must keep one
copy of the manifest, which has been signed by the generator and transporter
for each shipment of waste made to a hazardous waste facility. The original copy of the manifest must
accompany the waste shipment along with two additional copies. Once the disposal facility receives the
waste, the facility representative signs the manifest and returns it to the
generator. Clemson University must
retain the returned copy of the manifest signed by the receiving treatment,
storage or disposal facility for three years from the date of shipment. Copies of manifests for shipments of
hazardous waste sent out of South Carolina must be submitted to SCDHEC within
45 days of receiving the returned copy of the manifest from the disposal
facility.
D. Land Disposal Restriction
Certification
Listed and characteristic
hazardous wastes have been evaluated by EPA to determine their suitability for
land disposal. The result of this
evaluation is a treatment standard for each waste. Any waste meeting the treatment standards may be land
disposed without restriction in a RCRA land disposal unit. If the treatment standard for a waste
is not met, the waste cannot be land disposed without prior treatment.
Information defining the
restricted wastes and their treatment standards is available from the Manager
of Environmental Programs. Whether
the waste is restricted under the Land Disposal Restrictions 40 CFR Part 268
will be determined by testing the waste or using knowledge of the waste. At the time the waste is shipped for
off‑site disposal, a Notification and Certification Form must be
completed in full and must accompany the shipment. This form will identify the appropriate land disposal
treatment standards and whether or not these standards have been met.
All laboratory analyses used to
determine if a waste is subject to the land disposal restrictions will be
conducted in accordance with approved EPA test methods and procedures. For wastes with treatment standards
expressed as constituent concentrations in the waste extract (40 CFR 268.41),
waste residues or an extract of such residues will be tested using the toxicity
characteristic leaching procedure (TCLP).
For wastes with treatment standards expressed as constituent
concentrations in the waste (40 CFR 268.43), waste residues will be tested
using a total constituent analyses (TCA).
E. Placarding
Clemson University is
responsible for providing the transporter with the proper placards when
required to comply with DOT shipping and labeling requirements. If more than 1,000 pounds of flammable and/or combustible
material are offered for shipment at one time, the placards for flammable
and/or combustible material must be provided. The appropriate placards will be maintained at the facility
or will be purchased by Clemson University prior to shipping quantities
requiring placarding. Placards
must be located on all sides of the motor vehicle.
F. Record keeping and
Reporting
One copy of each manifest
prepared for a hazardous waste shipment must be kept at the facility until the
original signed copy is returned from the disposal facility which received the
waste. The copy signed by Clemson
University, the transporter and the receiving facility must be maintained at
the facility for three years from the date of shipment. If a hand‑signed copy is not
returned from the disposal facility within 35 days of the shipping date,
Clemson University must contact the transporter or the disposal facility to
determine the status of the hazardous waste.
If the completed manifest has
not been returned from the disposal facility within 45 days of the date the
waste was shipped from Clemson University, the Environmental Compliance Officer
will submit an Exception Report to SCDHEC. The report must contain a copy of the manifest retained by
Clemson University and a letter of explanation stating what efforts have been
made to locate the completed manifest and the results of those efforts.
All manifests and exception
reports must be maintained at the facility for at least three years from the
date the report was filed or the waste shipment was made.
VI. NON‑ROUTINE ACTIVITY
PROCEDURES
A. New Waste Streams
A new waste stream may be
generated in three ways:
á change in an existing process,
á implementation of a new process, or
á change in the regulations.
The generator, with the
assistance of the Environmental Compliance Officer, is responsible for
reviewing any new waste streams to determine if they will be subject to the
hazardous waste management regulations.
If the new waste stream is not excluded from regulation, analysis of a
waste stream sample may be required. Laboratory work may include analysis for
the hazardous waste characteristics outlines in Section II.
Knowledge of the process shall
be applied to determine analytical needs.
Analytical data will be reviewed to determine potential concerns of
ignitability or reactivity during storage. The generator is responsible for appropriately
characterizing all new waste streams generated in his area.
Professors, students and
employees shall notify the Environmental Compliance Officer if new waste
streams are to be generated.
B. Unlabeled Containers
The potential exists for
containers of unknown material to be discovered. Without knowledge of the container contents, appropriate
disposal options cannot be determined.
If an unidentified container is
discovered, the following steps shall be taken:
á Mark the container with the words "Awaiting
Administrative Determination" and date the container.
á Initiate a hazardous waste pickup.
á Immediately notify the Environmental Compliance
Officer to arrange for the container to be relocated to the Hazardous Waste
Accumulation Building.
If laboratory analysis is
required to appropriately characterize the waste material, a completed
"Sample Out for Analysis" label shall be affixed to the side of the
container (Figure VI‑1).
If the material is determined
to be a hazardous waste, label and date the container immediately, and properly
dispose of the material within 90 days.
Figure
VI-1
Sample Out-for-Analysis
Label
VII. TRAINING REQUIREMENTS
A. Who Must be Trained and
How Often
The regulatory framework which
identifies who must be trained may be circuitous, but must be complied with
nevertheless. 40 CFR 265.16 and 40
CFR 264.16 require training for personnel at interim status and permitted
hazardous waste management treatment, storage and disposal (TSD)
facilities. Hazardous waste
generators are instructed in 40 CFR 262.34(a)(4) to comply with the requirements
of 40 CFR 265.16 which is included in Appendix C of this manual. Therefore,
hazardous waste management training is required for personnel who work at
facilities which fit into any of the following categories:
á Permitted hazardous waste TSD facilities,
á Interim status hazardous waste TSD facilities,
á Large quantity generators.
Persons who must be trained
include those who are involved with or are occupationally exposed to hazardous
waste. This may include (but is
not limited to) persons who perform any of the following tasks:
á decide which wastes are hazardous waste,
á add hazardous waste into accumulation containers at
accumulation points,
á remove hazardous waste from accumulation containers,
á transport hazardous waste to or from accumulation
points,
á transport hazardous waste to or from storage units,
á respond to spills, fires or explosions involving
hazardous waste,
á complete hazardous waste manifests, annual reports or
exception reports,
á inspect hazardous waste accumulation points and storage
facilities,
á operate or work at accumulation points,
á work at permitted or interim status TSD facilities,
á conduct any tasks involving occupational exposure to or
which require management of hazardous waste.
The required training must be
successfully completed by all of the personnel described above. For new personnel, training must be
successfully completed within six months after assignment to the facility or to
a new position at the facility, whichever is later. Until that time, untrained personnel must not perform any
tasks involving hazardous waste management unless they are supervised by
trained personnel. Facility
personnel may be required to take part in an annual review of the entire training
program.
The Environmental Compliance Officer
will direct training of all applicable facility personnel in hazardous waste
management procedures. Included in
this training will be instruction in job specific hazardous waste management as
well as contingency plan implementation.
B. Scope of Mandatory
Training Requirements
There are two general
components to the training requirements in 40 CFR 265.16; personnel must be
trained:
1. How to perform their duties in a way that ensures the
facility's compliance with the regulations; and
2. How to respond to emergencies involving hazardous waste.
EPA regulations published in 40
CFR 265.16 regarding personnel training are presented in Appendix C of this
manual (separate document, copies available from EH&S).
C. Training Required by Other
Laws
Besides the required RCRA
training, other laws and regulations require training for many of the same
personnel who must receive RCRA training.
For example, persons working at permitted TSD facilities as well as hazardous
substance emergency response personnel are required to be trained in accordance
with OSHA regulations published in 29 CFR 1910.120. Personnel who work in areas in which hazardous chemicals are
present may be required to be trained in accordance with OSHA regulations
published in 29 CFR 1910.1200 or in accordance with substance specific
standards in 29 CFR 1910 Subpart Z. All employees who handle, prepare for
shipment, load, unload or drive a vehicle hauling DOT hazardous materials must
be trained in accordance with the DOT training requirements in 49 CFR
172.700-.704. These regulations
require initial general awareness, function-specific and safety training as
well as recurrent training every three years or when changes in the regulation
occur. To ensure that Clemson University personnel meet all of the training
requirements specified by environmental laws, the dean, director, department
head or supervisor, with guidance from the Environmental Compliance Officer,
should determine the necessary training required for associated employees.
D. Documentation and Training
Records
The following documents and
records must be maintained at Clemson University:
á The job title for each position at Clemson University
related to hazardous waste management including the name of the employee
filling the job.
á A written job description for each position listed
including the requisite skill, education or other qualifications, and duties of
personnel assigned to each position.
á A written description of the type and amount of
introductory and continuing training that will be given to each person filling
the listed position.
á Records documenting that the required training/job
experience has been given to, and completed by applicable Clemson University
personnel.
Training records on current
personnel must be kept until closure of the facility. Training records on former employees must be kept for at
least three years from the date the employee last worked at the facility. Personnel training records may
accompany personnel transferred to a different department within the
university.
APPENDIX A
(Remove this page and attach all current hazardous waste lists from SCDHEC regulation R.61-79 here)
CLEMSON UNIVERSITY HAZARDOUS
WASTE INCIDENT
CONTINGENCY PLAN
CLEMSON UNIVERSITY HAZARDOUS
WASTE INCIDENT
CONTINGENCY PLAN
Objective:
This SOP defines general
responsibilities of the first responding agencies of Clemson University to a
hazardous waste incident. It is intended to ensure safe and professional action
by those agencies who have responsibilities in hazardous waste response
situations.
Definition:
Hazardous wastes will be as
defined in R.61‑79.261 of the South Carolina Hazardous Waste Management
Regulations as revised. A hazardous waste incident may be defined as one of
these wastes and/or certain other wastes that may be leaking, spilled, burning,
reacting or having a release thereof, that may endanger life, property and/or
the environment.
Notification and Initial
Responsibility:
It will be the responsibility
of the first on the scene recognizing a hazardous waste incident to assess the
degree of life, property, and/or environmental safety hazard so that a preliminary
determination can be made as to notification and/or response by other agencies.
If the first on the scene
determines that a hazardous waste incident does exist, the following University
departments will be notified:
(1) Clemson University Fire Department 656‑2211
(2) Clemson University Police Department 656‑2222
(3) Environmental Health and Safety Department 656‑2583
EH&S Emergency
Coordinators:
Home
Phone (864) 654-2628, Work Phone (864) 656-1804
Secondary: Philip D. Carroll
Jr., 130 Mt. Bethel Rd., Pickens SC 29671
Home
Phone (864) 868-7412, Work Phone (864) 656-1770
First on Scene Procedures:
The first on scene recognizing
a potential hazardous waste incident shall make a brief assessment to
determine if:
(A) The situation can be resolved by those available with no danger to
persons, property and/or environment.
(B) A hazardous waste incident exists.
EVERY POTENTIAL
HAZARDOUS WASTE INCIDENT SHALL BE REPORTED TO ENVIRONMENTAL HEALTH AND SAFETY,
656‑2583.
In Event of a Hazardous
Waste Incident:
The first on scene recognizing
a hazardous waste incident shall be the on‑scene incident commander. That
person shall:
(1) EVACUATE the premises by activating the nearest FIRE ALARM pull box
and/or by shouting for others to vacate.
(2) NOTIFY the FIRE DEPARTMENT by FIRE ALARM pull box, and by
telephoning 656‑2211, with information about the incident. Also, NOTIFY
the POLICE DEPARTMENT (656‑2222).
(3) NOTIFY DEPARTMENT PERSONNEL who may assist with the emergency.
(4) NOTIFY ENVIRONMENTAL HEALTH AND SAFETY by telephoning 656‑2583.
(5) MEET AT THE FIRE DEPARTMENT COMMAND POST when it is established on
site and relinquish command to the CLEMSON UNIVERSITY FIRE DEPARTMENT.
THE CLEMSON UNIVERSITY FIRE
DEPARTMENT HAS THE AUTHORITY TO ASSUME COMMAND OF ANY HAZARDOUS
MATERIALS INCIDENT (ACT. NO. 65 OF 1983, SECTION 6‑11‑1450). The Fire Department will proceed
in accordance with CLEMSON UNIVERSITY FIRE DEPARTMENT STANDARD OPERATION PROCEDURES
NO. 1021, 3‑5.2, RESPONSE TO HAZARDOUS MATERIALS INCIDENTS.
Environmental Health and
Safety Department Responsibilities:
The Environmental Health and
Safety Department shall designate the Environmental Affairs Coordinator as
emergency coordinator in the event of a hazardous waste incident. That person
shall serve as support to the incident commander.
At all times, there must be at
least one employee either on the facility premises or on call (i.e., available
to respond to an emergency by reaching the facility within a short period of
time) with the responsibility for coordinating all emergency response measures.
This emergency coordinator must be thoroughly familiar with all aspects of the
facility's contingency plan, all operations and activities at the facility, the
location and characteristics of waste handled, the location of all records
within the facility, and the facility layout. In addition, this person must
have the authority to commit the resources needed to carry out the contingency
plan.
Emergency Procedures:
Whenever there is an imminent
or actual emergency situation, the coordinator (or his/her designee when the
emergency coordinator is on call) must immediately notify appropriate state or
local agencies with designated response roles if their help is needed.
(1) Whenever there is a release, fire or explosion, the emergency
coordinator must immediately identify the character, exact source, amount, and
extent of area involved. He/she may do this by observation or review of
facility records or manifests, and, if necessary, by chemical analysis.
(2) Concurrently, the emergency coordinator must assess possible hazards
to human health or the environment that may result from the release, fire or
explosion. This assessment must consider both direct and indirect effects of
the release, fire or explosion (e.g., the effects of any toxic, irritating, or
asphyxiating gases that are generated, or the effects of any hazardous surface
water run‑off from water or chemical agents used to control fire and heat‑induced
explosions).
(3) If the emergency coordinator determines that the facility has had a
release, fire or explosion which could threaten human health or the
environment, outside the facility, he/she must report his/her findings as
follows:
(A) If his/her assessment indicates that evacuation of local areas may
be advisable, he/she must immediately notify appropriate local authorities. He
must be available to help appropriate officials decide whether local areas
should be evacuated; and
(B) He/she must immediately notify SCDHEC (using its 24 hour number
803‑253‑6488).
The report must include:
(i) Name and telephone number of reporter;
(ii) Name and address of facility;
(iii) Time and type of incident (e.g., release,
fire);
(iv) Name and quantity of material(s) involved,
to the extent known;
(v) The extent of injuries, if any; and
(vi) The possible hazards to human health or the
environment, outside the facility.
(4) During an emergency, the emergency coordinator must take all
reasonable measures necessary to ensure that fires, explosions and releases do
not occur, recur or spread to other hazardous waste at the facility. These
measures must include, where applicable, stopping processes and operations,
collecting and containing release waste, and removing or isolating containers.
(5) If the facility stops operations in response to a fire, explosion or
release, the emergency coordinator must monitor for leaks, pressure buildup,
gas generation or ruptures in valves, pipes or other equipment wherever this is
appropriate.
(6) Immediately after an emergency, the emergency coordinator must
provide for treating, storing or disposing of recovered waste, contaminated
soil or surface water, or any other material that results from a release, fire
or explosion at the facility. Unless the owner or operator can demonstrate, in
accordance with South Carolina Hazardous Waste Management Regulations R.61‑79.261.3(c)
or (d), that the recovered material is not a hazardous waste, the owner or
operator becomes a generator of hazardous waste and must manage it in
accordance with all applicable requirements of R.61‑79.262 Standards
Applicable to Generators of Hazardous Waste, R.61‑79.263 Standards
Applicable to Transporters of Hazardous Waste and R.61‑79.264. (amended
11/90)
(7) The emergency coordinator must ensure that, in the affected area(s)
of the facility:
(A) No waste that may be incompatible with the released material is
treated, stored or disposed of until cleanup procedures are completed; and
(B) All emergency equipment listed in the contingency plan is cleaned
and fit for its intended use before operations are resumed.
(8) The owner or operator must notify SCDHEC (803‑253‑6488),
and appropriate state and local authorities, that the facility is in compliance
with paragraph (7) of this Section before operations are resumed in the
affected area(s) of the facility.
(9) The owner or operator must note in the operating record the time,
date and details of any incident that requires implementing the contingency
plan. Within 15 days after the incident, he/she must submit a written report on
the incident to the department. The report must include:
(A) Name, address, and telephone number of the owner or operator;
(B) Name, address, and telephone number of the facility;
(C) Date, time, and type of incident (e.g., fire, explosion);
(D) Name and quantity of material(s) involved;
(E) The extent of injuries, if any;
(F) An assessment of actual or potential hazards to human health or the
environment, where this is applicable; and
(G)
Estimated
quantity and disposition of recovered material that resulted from the incident.
Evacuation Plans: Entire campus plans are too
numerous for inclusion here in this document.
Individual building plans,
including evacuation floor plans, are maintained and copies can be
obtained at no charge from:
Environmental Health and Safety, Clemson University, Moorman
House, 208 N. Palmetto Blvd.,
Clemson SC., 29631-3012. (864) 656-2583, fax # (864) 656-
7630. These plans must be
obtained and the maps posted at each Accumulation Point. These
plans are needed by other
regulations and may require more extensive posting. For information
on these contact the University
Fire Marshal at (864) 656-2323 and the Chemical Hygiene
Officer at (864) 656-7554 for
compliance with these other regulations.
Vermiculite
20 bags
Oil dry 2 bags
Aggressive fluids Spill kit
Large for up to 65 gallons
Non Aggressive fluids Spill
kit Large for up to 65 gallons
Non Sparking Shovels (2)
Drain Blockers 24ÓX 24Ó pads
(2)
Drain Plugs 4Ó (4)
Portable Spill kit
Aggressives (on Truck)
Broom and Dust pan (one also
on truck)
85 gallon over pack drums (4)
Nitrile Gloves
Coated Tyvex Coveralls
Non Sparking bronze tool kit
(on truck)
Barrel leak plug kit (on
truck)
First Aid kit (on truck)
20 # ABC Fire extinguisher
(on truck)
Numerous plastic pans and
contaniers of various sizes for repackaging or over packing
Full face respirators
(individually assigned during fit testing)
Drum funnels and absorbent
pads of assorted sizes
Barrel containment spill pans
Spill controll pallets,
plastic, numerous sizes
Waterproof tarps for above
(6)
One fork lift with numerous
barrel handling attachments
Drum sampling pipettes (10)
Mercury spill kits (2)
One-non aggressive fluids
Spill kit Large for up to 65 gallons
One aggressive fluid Spill
kit Large for up to 65 gallons
Nitrile gloves- several cases
One 30 gallon Hepa-filtered
Vacuum
One Flammable fluid pump,
electric
Two flammable fluids pumps,
Pneumatic
One portable air compressor
Two Scott air pak‰- SCBAÕs
Lab coats- three each
Safety glasses- 20 pairs
One fork lift with numerous
barrel handling attachments
First aid kit
Tool box with assorted tools
Full-face respirators
(individually issued at fit testing)
pH meter
Spill containment pallets,
numerous sizes
Hazardous
Waste Management Regulations
(Separate Documents)
For Copies of these documents to maintain a
departmental library, contact Environmental Health and Safety at (864) 656-2583
APPENDIX
C - Table of Contents
The following federal
regulations (or parts thereof) concerning the management of hazardous waste are
included in this appendix:
|
40 CFR 261 |
IDENTIFICATION AND LISTING OF
HAZARDOUS WASTE |
|
40 CFR 262 |
STANDARDS APPLICABLE TO
GENERATORS OF HAZARDOUS WASTE |
|
40 CFR 264 264.16; SUBPART C,D & I |
STANDARDS FOR OWNERS AND
OPERATORS OF HAZARDOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES |
|
40 CFR 265 265.15; SUBPART C,D & I |
INTERIM STATUS STANDARDS FOR
OWNERS AND OPERATORS OF HAZARDOUS WASTE TREATMENT, STORAGE, AND DISPOSAL
FACILITIES |
|
40 CFR 279 |
STANDARDS FOR THE MANAGEMENT
OF USED OIL |
|
49 CFR 172.700-.704 |
DOT TRAINING REQUIREMENTS |
|
29 CFR 1910.120 |
OSHA HAZARDOUS WASTE
OPERATIONS AND EMERGENCY RESPONSE |
APPENDIX D
Hazardous
Waste Storage
and other Miscellaneous
Information