A floating containment boom holding back oil and debris on a creek, photographed for EPA DOCUMERICA in the 1970s

The slick leaves. The chemistry stays in the sand.

Shoreline crews recover what can be lifted, and they are good at it. What survives their last pass is hydrocarbon chemistry bound into sand, shingle and marsh sediment, on ground too dispersed to lift. SoilScrubber works that fraction where it lies.

The residual

What the last recovery pass leaves behind.

The US Environmental Protection Agency classes petroleum hydrocarbons as priority pollutants. They arrive as a mixture — alkanes, polycyclic aromatic hydrocarbons, resins, asphaltenes — and some of those components are carcinogenic, mutagenic or teratogenic.

On a beach the awkward part is physical. Hydrocarbons sorb hard to soil organic matter and sit encapsulated in the mineral around them, which is what makes a stretch of shore keep testing dirty for years after it stops looking dirty. The material is too dispersed to lift and too bound to rinse.

It is also, chemically, the same problem SoilScrubber already answers on playa and exposed lakebed. The ground stays put. The chemistry it carries does not have to.

The published position

What the literature supports, stated as it stands.

A 2020 review in Chemosphere surveyed advanced oxidation across ozone, Fenton, persulfate, non-thermal plasma and wet oxidation as applied to petroleum-hydrocarbon-contaminated soils. It names no operator and tests no equipment of ours. Three of its findings bear on an oiled shore.

Demonstrated at three scales

The review concludes that advanced oxidation has been shown at laboratory, pilot and full scale to be a feasible method for remediating these soils. That is a statement about a family of processes, and it settles feasibility rather than performance on any particular shore.

Coarse, dry ground suits ozone

Ozone carries high mass transfer efficiency and suits in-situ work on soil with low moisture, low organic matter and coarse particles, moving through contaminated ground more easily than a liquid reagent. Beach sand and shingle are that description.

The intermediates are the open question

Its own caution: the figure studies reported was hydrocarbon removal, while the toxic transformation products formed along the way stayed outside the measurement. One non-thermal plasma system degrading gasoline threw 14 byproducts. A scope written on this ground measures them alongside the parent load.

US$67.0bn BP's cumulative pre-tax charge for Deepwater Horizon by the end of 2018, covering response, settlements and litigation BP plc Form 20-F, FY2018, filed with the SEC
14 Byproducts detected in one non-thermal plasma system degrading gasoline, chiefly 2-methylpentane, 3-methylpentane and hexane Zhang et al., Chemosphere 246, 2020

The assist

Who does what on an oiled shore.

A response plan already has a shoreline section, an incident command and an exercise schedule behind it. The assist slots into that structure and answers to it.

Responders hold recovery, access, wildlife and the decision to work a stretch at all. A SoilScrubber crew arrives after them, on ground they release, and treats the oxidizable toxic fraction in place. Sand stays where it is, in the same quantity, chemically altered.

Out in the water, a ChemSlayer hull works the leachate and the oxygen debt under a slick. Neither system does the other's job, and an operator can be asked for both.

Aerial view of a remote arid coastline where pale sand meets turquoise water
Coarse, low-organic sand: the profile the published ozone work suits, and the profile most exposed shorelines present.

Scope

Where the assist stops.

Six limits, each of which belongs in a response plan before an incident, where they cost nothing to read.

  • It does not recover oil. Booms, skimmers, sorbents, in-situ burning and the crews working oiled ground by hand are the recovery trade, and they keep it.
  • It does not mineralize a hydrocarbon load in a pass. Sorption onto organic matter is what the published work says makes full mineralization reagent-hungry, and a scope is written against a measured fraction instead.
  • It does not carry a removal percentage, a clean-up date or a shoreline treatment ranking. The first number for your shore is measured on it.
  • It does not rest on an Alarivean field record. No oiled-shoreline program has run. The support is published chemistry on this class of soil, and the calibration is yours.
  • It does not touch the metals fraction of a sediment. A hydroxyl radical changes organic chemistry and leaves an element where it found it.
  • It does not claim a health or ecological recovery outcome. Sampled material gets a laboratory number. Attributing what follows on the shore to a treatment program is somebody else's science.

How a shoreline scope gets settled

The sequence is the one every SoilScrubber program runs, with a response plan sitting over it. A sampled inventory of the affected ground comes first: what is in it, at what concentration, across which stretch. A control area is marked out and left untreated. The protocol, the sampling intervals and the laboratory are agreed in writing before the first pass, and the authority holding the shoreline reads the record as the crew does.

Timing is the one thing a client controls that we cannot. A stretch released weeks after an incident is a different chemical problem from the same stretch released after two winters, because weathering has already taken the volatile fraction and left the heavier compounds bound tighter. Both are workable. They are not the same scope, and a plan written before an incident is what keeps that choice open.

An incident is a legitimate way to arrive, and plenty of programs will begin exactly there. The engagement is still a subscription, because the case for standing capability outlives the event that prompted it: while the traffic, the terminal or the field that produced one release is still operating, a system already in the region works a shore in days, and a system assembled from scratch does not. The minimum subscription period for shore work runs on a shorter cycle than a basin-scale aquatic prosperity program, and its length sits in the agreement.

How a SoilScrubber program runs, stage by stage

The published work behind this

  1. Zhang, Liu, Zhong & Zhang — AOPs-based remediation of petroleum hydrocarbons-contaminated soils: efficiency, influencing factors and environmental impacts, Chemosphere 246, May 2020. Review article; the abstract, highlights and conclusions are open, and the full text sits behind the publisher's paywall.
  2. BP plc — Form 20-F for FY2018, filed with the US Securities and Exchange Commission, for the cumulative Deepwater Horizon charge.
Rocky arid coastline meeting calm turquoise sea under a clear sky

Next step

Put the ground question in the plan before the incident.

Send the stretch of shore you are responsible for, its material, and whatever sediment analysis exists. Back comes a read on whether an oxidation assist suits that ground, what a control area would have to show, and where it belongs in your response plan.