[ ⌜ 01 // SUBSURFACE INVASIVE DRILLING ⌝ ]

GEOPROBE DRILLING & GROUNDWATER WELL NETWORKS

HYDRAULIC DIRECT-PUSH CORING • LOW-FLOW GROUNDWATER PURGING • HELIUM SHROUD TO-15 VAPOR PROBES

When a Phase I ESA identifies a Recognized Environmental Condition (REC), guesswork must be replaced with empirical chemistry. Envirogyn deploys track-mounted Geoprobe direct-push hydraulic rigs to extract undisturbed soil cores, install groundwater monitoring networks, and collect vapor intrusion samples with minimal surface disturbance.

Geoprobe Direct-Push Hydraulic Soil Boring Rig Operating on Commercial Site GEOPROBE 7822DT RIG

Continuous Macro-Core Soil Borings

Extracting continuous 4-foot or 5-foot soil cores in disposable PETG liners down to 15–30+ feet below ground surface (bgs). Certified environmental geologists perform Unified Soil Classification System (USCS) lithologic logging and photoionization detector (PID) headspace field screening at 0.1 ppm sensitivity.

  • • Undisturbed lithology: Beaumont clay, sand lenses, silt stratification
  • • PID 10.6 eV lamp screening to isolate highest volatile hydrocarbon intervals
  • • Zero-headspace En Core / Terra Core preservation for volatile organics (EPA 5035A)
Environmental Professional Inspecting Core Sample in Field for Stratification and Chemical Odors LITHOLOGIC SAMPLE AUDIT

Monitoring Wells & Vapor Probes

Installing temporary hydropunch samplers or permanent 2-inch Schedule 40 PVC monitoring wells. Sampling via low-flow peristaltic pumps with field parameter stabilization (pH, DO, ORP, turbidity, conductivity) under strict EPA Low-Flow protocols.

  • • Water table gauging and gradient flow direction calculation
  • • Sub-slab soil vapor pins for TO-15 passivated 6-Liter Summa canisters
  • • Helium shroud real-time leak testing to guarantee sample integrity
[ ⌜ 02 // ANALYTICAL LABORATORY SUITES ⌝ ]

THE 5 TARGET CONTAMINANT PANELS

EPA METHOD 8260D • METHOD 8270E • TX-1005 • RCRA 8 • PFAS EPA 1633

All samples are dispatched under unbroken, tamper-evident Chain of Custody to state-certified NELAP environmental chemistry testing benches. Data is delivered in court-defensible Level II through Level IV quality control validation packages.

[ EPA METHOD 8260D / 5035A ]

Volatile Organic Compounds (VOCs)

Full scan for gasoline hydrocarbons, chlorinated solvents, and industrial degreasers:

  • • Benzene, Toluene, Ethylbenzene, Xylenes (BTEX)
  • • Tetrachloroethene (PCE / "Perc" dry cleaner solvent)
  • • Trichloroethene (TCE / degreaser) & cis-1,2-DCE
  • • Vinyl Chloride (toxic breakdown metabolite)
  • • Methyl Tert-Butyl Ether (MTBE)
[ TxDOT METHOD TX-1005 ]

Total Petroleum Hydrocarbons (TPH)

Texas state-specific carbon fraction fingerprinting for fuel oils and underground tanks:

  • • C6–C12 Gasoline Range Organics (GRO)
  • • >C12–C28 Diesel Range Organics (DRO)
  • • >C28–C35 Heavy Lube Oil & Motor Oil Range
  • • Total Hydrocarbon Summation under TRRP PCLs
  • • Silica Gel Cleanup option for biogenic interference
[ EPA METHOD 8270E / 3510C ]

Semi-Volatiles & PAHs (SVOCs)

Heavy industrial distillates, creosote, coal tars, and chemical manufacturing residues:

  • • Polycyclic Aromatic Hydrocarbons (PAHs)
  • • Benzo(a)pyrene, Chrysene, Fluoranthene
  • • Naphthalene & 2-Methylnaphthalene
  • • Phenols, cresols, and chlorinated benzenes
  • • Polychlorinated Biphenyls (PCBs via EPA 8082A)
[ EPA METHOD 6020B / 7471B ]

RCRA 8 Heavy Toxic Metals

Inductively Coupled Plasma Mass Spectrometry (ICP-MS) and Cold Vapor Mercury analysis:

  • • Arsenic (As) • Lead (Pb) • Cadmium (Cd)
  • • Chromium (Total & Hexavalent Cr VI)
  • • Mercury (Hg) via Cold Vapor atomic absorption
  • • Barium (Ba) • Selenium (Se) • Silver (Ag)
  • • Synthetic Precipitation Leaching Procedure (SPLP)
[ EPA METHOD 1633 / 537.1 ]

Emerging Contaminants (PFAS / PFOA)

"Forever chemicals" from aqueous film-forming foam (AFFF), metal plating, and textiles:

  • • Perfluorooctanoic Acid (PFOA) • PFOS
  • • GenX chemicals, PFHxS, PFNA, PFBS
  • • 1,4-Dioxane (stabilizer for chlorinated solvents)
  • • Parts-per-trillion (ppt) ultra-trace detection
  • • Strict non-fluoropolymer field sampling protocol
[ LEGAL INTEGRITY CRITERIA ]

Court-Defensible Data Validation

Laboratory verification packages engineered to withstand adversarial courtroom cross-examination:

  • • Unbroken electronic and physical Chain-of-Custody (eCoC)
  • • Trip blanks, field blanks, equipment rinsates & duplicates
  • • Matrix Spike / Matrix Spike Duplicates (MS/MSD)
  • • Certified surrogate recoveries & initial calibration verifications
  • • Data usability summary reports (DUSR) prepared by Senior Chemists
[ ⌜ 03 // REGULATORY BENCHMARK COMPARATOR ⌝ ]

TCEQ TIER 1 PCL SCREENING COMPARATOR

30 TAC CHAPTER 350 • PROTECTIVE CONCENTRATION LEVELS (PCLs) • RESIDENTIAL VS COMMERCIAL

The Texas Risk Reduction Program establishes chemical concentration thresholds across three exposure pathways: Soil leaching to Groundwater (SoilGWIng), Groundwater Ingestion (GWGWIng), and Direct Inhalation/Ingestion (SoilInh+Ing). Filter by contaminant category below to inspect critical Texas regulatory benchmarks.

Target Contaminant CAS Number Groundwater Ingestion (GWGWIng) Soil-to-GW Leaching (SoilGWIng) Direct Soil Inh+Ing (Commercial) Regulatory Action Level
Benzene (Gasoline VOC) 71-43-2 0.005 mg/L (5 ppb) 0.03 mg/kg 99 mg/kg > 5 ppb Triggers VCP / Remediation
Toluene (Gasoline Component) 108-88-3 1.0 mg/L (1,000 ppb) 12 mg/kg 16,000 mg/kg UST Closure Standard
Total Petroleum Hydrocarbons (TX-1005) MIXTURE 5.0 mg/L 100 mg/kg (PST Tier 1) 10,000 mg/kg > 100 mg/kg LPST Filing Required
Tetrachloroethene (PCE / Dry Cleaning) 127-18-4 0.005 mg/L (5 ppb) 0.05 mg/kg 350 mg/kg > 5 ppb Vapor Intrusion Audit
Trichloroethene (TCE / Degreaser) 79-01-6 0.005 mg/L (5 ppb) 0.01 mg/kg 61 mg/kg High Vapor Intrusion Risk
Vinyl Chloride (Chlorinated Metabolite) 75-01-4 0.002 mg/L (2 ppb) 0.001 mg/kg 6.2 mg/kg Carcinogenic Emergency Pathway
Lead (Total Inorganics) 7439-92-1 0.015 mg/L (Action Level) 15 mg/kg 1,600 mg/kg (Comm) / 500 (Res) SPLP Leaching Test Triggered
Arsenic (Herbicide / Industrial) 7440-38-2 0.010 mg/L (10 ppb) 5.9 mg/kg (Gulf Coast Bkgd) 200 mg/kg Background Comparison Protocol
PFOA & PFOS (AFFF Firefighting Foam) 335-67-1 / 1763-23-1 0.000004 mg/L (4 ppt EPA MCL) 0.001 mg/kg 1.0 mg/kg Ultra-Trace EPA CERCLA Rule
TIER 1 SCREENING (NO ACTION)

If analytical concentrations remain strictly below residential Tier 1 PCLs, the site qualifies for unconditional regulatory closure with No Further Action (NFA).

TIER 2 SITE-SPECIFIC MODELING

If Tier 1 levels are exceeded, Envirogyn calculates Tier 2 PCLs utilizing site-specific soil fraction organic carbon (foc), depth to groundwater, and hydraulic conductivity.

STATUTORY EXIT ENROLLMENT

Where exceedances persist, Envirogyn models remediation engineering plans and orchestrates entry into the TCEQ Voluntary Cleanup Program (VCP) to secure legal release of liability.

[ ⌜ 04 // EXIT STRATEGIES & COST MODELING ⌝ ]

TCEQ REGULATORY CLOSURE & REMEDIATION EXIT

TCEQ VOLUNTARY CLEANUP (VCP) • INNOCENT OWNER PROGRAM (IOP) • MUNICIPAL SETTING DESIGNATIONS (MSD)

A Phase II ESA is not merely an investigative report—it is the strategic roadmap for transaction execution. When chemical impacts are confirmed, Envirogyn models remedial engineering costs and navigates institutional state programs to release owners from ongoing liability.

[ 30 TAC § 333 // TCEQ VCP ]

Voluntary Cleanup Program (VCP)

Enables commercial property owners to remediate pollution under state oversight. Upon completion, the TCEQ issues a statutory Certificate of Completion (COC) that legally releases all future non-responsible lenders and buyers from liability to the State of Texas.

BENEFIT: Eliminates state enforcement risk for future property transferees.
[ TEXAS HEALTH & SAFETY CODE § 361 ]

Innocent Owner/Operator Program (IOP)

For properties contaminated solely by off-site migrating plumes (e.g., an uphill gas station or neighboring industrial yard). Envirogyn prepares the site investigation report to secure a formal Certificate of Innocent Ownership from the TCEQ.

BENEFIT: Unconditionally shields owner from remediation expenses.
[ TCEQ WATER CODE CH. 361 SUBCH. W ]

Municipal Setting Designation (MSD)

Prohibits the use of shallow groundwater for potable drinking purposes within a designated municipal perimeter. Eliminating the groundwater ingestion pathway (GWGWIng) allows higher residual contaminant concentrations to remain in place legally, saving millions in active pump-and-treat costs.

BENEFIT: Closes contaminated groundwater sites without massive excavation.
⌜ FINANCIAL FIDUCIARY PROTECTION ⌝

Remediation Cost Modeling & Escrow Quantification

If contamination is detected during closing due diligence, Envirogyn provides defensible Class 4 and Class 3 remedial cost estimates (AACE International standards). We model Soil Vapor Extraction (SVE), Dual-Phase Extraction (DPE), In-Situ Chemical Oxidation (ISCO), and targeted source excavation to establish precise contractual escrow holdbacks or price concessions.

[ ⌜ 05 // INTEL BRIEFING ⌝ ]

PHASE II ESA TECHNICAL FAQ

INVASIVE SAMPLING, DRILLING PROTOCOLS & REGULATORY REPORTING REQUIREMENTS
[Q1] What is the turnaround time for Phase II analytical laboratory results? ▾
Standard analytical laboratory turnaround is 5 to 7 business days from sample receipt. For emergency transaction deadlines, Envirogyn offers STAT expedited analytical turnarounds including 24-hour and 48-hour rush options through our partner NELAP-accredited chemical testing laboratories.
[Q2] Will Geoprobe drilling cause structural damage to concrete slabs or parking lots? ▾
No. Direct-push Geoprobe rigs utilize hydraulic percussion to advance small-diameter tooling (typically 2.25 inches in diameter). When coring through concrete slabs or asphalt, a diamond-tipped core drill creates a clean, circular penetration. Upon completion of sampling, every borehole is pressure-grouted with bentonite slurry to the surface and neatly patched with matching concrete or cold-patch asphalt, restoring full load-bearing integrity.
[Q3] What happens if Phase II sample results exceed TCEQ Tier 1 PCLs? ▾
An exceedance does not necessarily require massive active excavation. In Texas, the TRRP framework permits Tier 2 site-specific risk adjustments (e.g., proving the groundwater is non-potable or encapsulated under an engineered pavement cap). Envirogyn assists clients in modeling exposure pathways, implementing Activity and Use Limitations (AULs), or enrolling in the Voluntary Cleanup Program (VCP) to secure closing clearance.
[Q4] Does Envirogyn report Phase II results directly to the TCEQ or EPA? ▾
No. In Texas, Environmental Professionals performing private commercial due diligence are bound by strict client confidentiality. Unless an immediate, life-threatening imminent hazard exists, the statutory obligation to report a historical release to the TCEQ rests with the property owner or operator under the Texas Water Code, not the independent consulting investigator.
[Q5] What is the difference between a Temporary Hydropunch and a Permanent Monitoring Well? ▾
A Temporary Hydropunch advances a slotted drive point directly into the groundwater table, extracts a grab sample via peristaltic tubing, and is immediately pulled and grouted during a single mobilization—minimizing cost and site disturbance. A Permanent Monitoring Well consists of a 2-inch PVC casing, sand pack, bentonite seal, and flush-mount steel vault installed to enable recurring quarterly water level gauging and trend monitoring over months or years.
[ ⌜ DISPATCH COMMAND // INVASIVE RECON ⌝ ]

COMMISSION A PHASE II SUBSURFACE INVESTIGATION

Eliminate environmental uncertainty before committing institutional capital. Deploy Geoprobe direct-push rigs, groundwater monitoring, and vapor screening across the Texas Gulf Coast.