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SU0002684
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SU0002684
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Entry Properties
Last modified
5/7/2020 11:29:24 AM
Creation date
9/5/2019 10:40:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0002684
PE
2633
FACILITY_NAME
SA-99-56
STREET_NUMBER
1300
Direction
N
STREET_NAME
GERTRUDE
STREET_TYPE
AVE
City
STOCKTON
APN
14327067
ENTERED_DATE
10/31/2001 12:00:00 AM
SITE_LOCATION
1300 N GERTRUDE AVE
QC Status
Approved
Scanner
SJGOV\rtan
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\MIGRATIONS\G\GERTRUDE\1300\SA-99-56\SU0002684\APPL.PDF \MIGRATIONS\G\GERTRUDE\1300\SA-99-56\SU0002684\CDD OK.PDF \MIGRATIONS\G\GERTRUDE\1300\SA-99-56\SU0002684\EH COND.PDF \MIGRATIONS\G\GERTRUDE\1300\SA-99-56\SU0002684\EH PERM.PDF
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EHD - Public
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Mr. Michael Serra <br /> December 22, 1999 <br /> Page 2 <br /> B) Applying knowledge in light of the materials or processes used in <br /> generating the waste. <br /> In addition, 22 CCR section 66260.200(c), allows a generator to self-classify their waste <br /> as a result of their findings as described above and manage the waste in accordance <br /> with that classification. When self-classifying their waste, a generator need not provide <br /> notification to the Department of Toxic Substances Control (DTSC) of their intention to <br /> do so. However, if a generator wishes to obtain a concurrence from DTSC pursuant to <br /> 22 CCR section 66260.200(d), the generator must submit to DTSC for review that <br /> information which is required by 22 CCR section 66260.200(m). Until the DTSC <br /> completes its assessment of the information submitted in support of a concurrence <br /> pursuant to 22 CCR section 66260.200(d), the generator of the waste must manage the <br /> waste as hazardous waste. <br /> In this particular case, you and Mr. Murillo presented me with a packet of various types <br /> of information related to the fly ash. Much of it was informational in nature, but included <br /> only a limited amount of analytical data. While no final conclusion with respect to the <br /> characteristics of the fly ash can be drawn from the analytical data presented, it appears <br /> to indicate (on a preliminary basis) that the fly ash may not exhibit the federal Toxicity <br /> Characteristic (TC) as measured by the Toxicity Characteristic Leaching Procedure <br /> (TCLP) pursuant to 22 CCR section 66261.24(x)(1), nor exhibit the characteristic of <br /> corrosivity pursuant to 22 CCR section 66261.22(a)(3). <br /> As I mentioned in our December 1 meeting that a more comprehensive evaluation or <br /> analysis of the fly ash may be warranted. More specifically, Chapter 11 ,Division 4.5, 22 <br /> CCR outlines the requirements and criteria to determine when a waste is identified as a <br /> hazardous waste. The Chapter 11 criteria include the characteristics of toxicity (acute <br /> and chronic), reactivity, ignitability, and corrosivity. If the waste exhibits one or more of <br /> these aforementioned characteristics, the waste is classified as hazardous waste and <br /> must be managed as such. Therefore, to ensure that the fly ash is properly <br /> characterized, I would recommend that the following analytical testing be performed or <br /> continue to be performed on a minimum of four representative samples of the fly ash: <br /> 1) The TC as measured by the TCLP pursuant to 22 CCR section <br /> 66261 .24(a)(1); <br /> 2) The characteristic of corrosivity (for solids) pursuant to 22 CCR section <br /> 66261.22; <br /> 3) The characteristic of acute toxicity as measured by the aquatic bioassay <br /> pursuant to 22 CCR section 66261.24(a)(6); <br /> 4) A measurement of the total concentration of the persistent and <br /> bioaccumulative toxic substances pursuant to 22 CCR section <br /> 66261 .24(a)(2)(A);and, <br /> 5) A measurement of the soluble concentration of the persistent and <br /> bioaccumulative toxic substances as measured by California's Waste <br /> Extraction Test (WET) pursuant to 22 CCR section 66261.24(a)(2)(A). <br />
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