ESA study materials
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ESA flashcards

ESA · Build recall with a focused review session.

32 cards. Read the term and the definition here. The deck at the top of this page is optional.

CERCLA strict liability
CERCLA imposes liability without regard to fault on current owners, past owners at disposal time, arrangers, and transporters; liability may be joint and several and retroactive.
Bona fide prospective purchaser
A CERCLA defense for buyers who conduct all appropriate inquiries before acquisition, have no affiliation with liable parties, and satisfy continuing obligations including reasonable steps.
Security interest exemption
Protects lenders holding indicia of ownership primarily to protect a security interest from CERCLA liability, provided they do not participate in management of the facility.
RCRA cradle to grave
RCRA Subtitle C regulates hazardous waste from generation through transportation to treatment, storage, and disposal, imposing manifest and permit requirements on each handler.
EPCRA reporting thresholds
EPCRA requires facilities storing hazardous chemicals above threshold quantities to report under Sections 311 and 312 and to submit Toxics Release Inventory data under Section 313.
All appropriate inquiries
AAI under 40 CFR Part 312 requires a Phase I conducted or updated within one year before acquisition, with interviews, records review, and site visit within 180 days.
ASTM E1527-21 scope
The standard defines the Phase I process: records review, site reconnaissance, interviews, and a report identifying RECs, CRECs, HRECs, de minimis conditions, and data gaps.
Standard database search radii
ASTM E1527-21 specifies minimum search distances, such as one mile for NPL sites and one-eighth mile for RCRA generators, with larger radii for some listings.
Historical REC definition
An HREC is a past release that has been addressed to unrestricted use without engineering or institutional controls; it does not require action but must be disclosed.
Controlled REC definition
A CREC is a REC that has been addressed but where engineering or institutional controls may be required to protect human health or the environment.
Environmental professional declaration
The report must include a signed declaration that the assessment meets AAI standards and that the professional meets the qualifications in 40 CFR 312.10.
REC identification rationale
Each REC must be documented with reasoning connecting the observed or historical condition to a release or potential release of hazardous substances or petroleum products.
Sanborn map use
Historical fire insurance maps can reveal past USTs, dry cleaners, gasoline stations, and industrial uses that are not visible in current site conditions.
City directory research
City directories provide year-by-year occupancy records used to corroborate historical uses and identify tenants such as dry cleaners or auto repair shops.
Business environmental risk
A BER is a condition that may present a business risk but does not meet the REC definition; it is reported separately and does not trigger the same disclosure obligations.
De minimis condition
A de minimis condition is a release that does not pose a threat to human health or the environment and does not meet the REC threshold for action.
Conceptual site model
The CSM identifies contaminant sources, release mechanisms, exposure pathways, and receptors, guiding sampling locations, analytes, and risk evaluation for a Phase II.
Low-flow groundwater sampling
Low-stress purging and sampling minimizes turbidity and disturbance, producing more representative dissolved-phase concentrations than high-flow purging methods.
QA/QC field samples
Quality assurance includes field duplicates, trip blanks, equipment blanks, matrix spikes, and chain-of-custody records to support defensible analytical data.
Field screening limitations
PID, FID, and OVA readings indicate volatile organic compound presence in real time and guide sample selection but are not definitive analytical results.
DNAPL behavior
Dense non-aqueous phase liquids such as PCE and TCE sink below the water table and can persist as long-term continuing sources of dissolved contamination.
LNAPL behavior
Light non-aqueous phase liquids such as gasoline float on the water table and spread laterally with groundwater flow, affecting downgradient receptors.
Fate and transport processes
Advection, dispersion, sorption, volatilization, biodegradation, and abiotic transformation govern how contaminants move and attenuate in soil and groundwater.
Hazard quotient formula
The hazard quotient equals the exposure dose divided by the reference dose; a value greater than one indicates potential noncarcinogenic concern requiring further evaluation.
Carcinogenic risk calculation
Carcinogenic risk is estimated as exposure dose times the cancer slope factor or inhalation unit risk, with target risk ranges typically from 1E-06 to 1E-04.
Report findings categories
Phase I reports must distinguish RECs, CRECs, HRECs, de minimis conditions, and BERs, with an opinion on whether the property qualifies for liability protections.
Data gap disclosure
The report must identify data gaps, state whether each affects the ability to identify RECs, and document whether the gap was resolved or remains.
Documentation retention
Retaining maps, photographs, database reports, and correspondence supports defensibility and is essential if the assessment is later challenged in litigation.
Due diligence tailoring
Due diligence scope should reflect transaction type, historical use, buyer risk tolerance, and lender requirements, with the Phase I satisfying AAI timing rules.
Environmental insurance types
Pollution legal liability, cost cap, and remediation stop-loss policies transfer environmental risk identified during due diligence to an insurer for a premium.
Risk allocation tools
Purchase price adjustments, escrows, indemnities, and representations and warranties allocate environmental risk between buyer and seller in a transaction.
State voluntary cleanup programs
VCPs can provide liability relief and closure letters, but the scope, standards, and protections vary significantly among states and must be verified case by case.