Level 2 or Phase 2Environmental Site AssessmentTake this Self Test (For your Eco-Crisis Management Skills) While putting in a new power service on your property, you find a large, oily smelling, mostly empty, underground tank - who gets your call? (click on the box below with your answer)
The term "Level 2" is not really a legal or technical term, but it is commonly used to identify a report that usually contains the analysis of soil or water samples by a qualified laboratory for the concentration of known hazardous substances. The "level" of the assessment will depend somewhat on the ability of the local environment to absorb or mitigate problems on its own. More commonly the state government has published "guidelines" or "rules" defining the legal maximum contaminant level or MCL allowed in soil or groundwater based on toxicity studies and other statistical analyses. These maximums are sometimes referred to as cleanup levels or action levels and form the basis for determining that a site has been "cleaned-up" (another term seldom found in a competent environmental report.) All known hazardous substances have such levels defined by state rules. For example a common MCL for gasoline in soil is now 100 mg/kg (or 100 parts per million) whereas the MCL for just the Benzene portion of the gasoline in groundwater is 1 µg/L (one part per billion.) Sites that involve the potential contamination of groundwater will likely be radically more difficult and expensive to achieve a "no further action" level than sites with soil contamination only. Why do I have to do this testing? If you must do a level 2 site assessment, there may already be the suspicion of a problem on your site. Perhaps a level 1 assessment indicated a problem on your or nearby property. Perhaps an undesirable sample has been drawn from a neighbor's water well. A level 2 assessment can also mean that your state department of ecology or environment has been contacted and may have ordered this investigation based on the follow-up of a complaint. There could be a regional groundwater issue or some other contamination issue and certain property owners may have been identified based on the predicted or known flow path of a known substance. Banks are often more strict than government agencies on certain environmental issues, and a simple refinancing may involve a lender or an underwriter's requirement for such a test on commercial property. An owner may also voluntarily order a report for due diligence based on advice or suspicion that a nearby activity may have affected his or her property. Is this an environmental impact assessment? A Level 2 or Phase 2 environmental site assessment can sometimes be considered an impact assessment. Sometimes the same activity can be called a cleanup. The assessment can also be an instrumental part of the planning process in large scale projects. The scope of such studies can be broad and difficult to predict depending on the details of the site and the project, and the characteristics of the of the potential hazard.
The scale and therefore the cost of the sampling will vary widely depending on whether significant multidisciplinary or complex environmental issues are present. However a figure credited to the World Bank for large scale projects is the one per-cent rule based on the cost of construction not including operational accidents. Costs will be lower if the assessment is done before significant construction has started. The cost of a smaller scale assessment will be determined by the assessor based on the likelihood of encountering a known hazard. There will be no guarantee of a "clean" site. The only way to prove a site clean is to excavate 100% of the area, an unrealistic idea. A plan for a logical pattern of samples must be designed with the goal of performing a diligent search for potential environmental conditions. There is no standard way of laying out a pattern or depth of sample locations except in the case of very common sites such as gas stations and the systematic removal of obsolete and leaking underground storage tanks (LUST.) These sites involve standard sizes, capacities and other conditions. For instance, when removing underground fuel storage tanks, sampling the soil in the walls and along the bottom of the excavated cavity for each tank is logical strategy and covered by standard state rules and a standard number of samples. Almost all other Level 2 sites will require thought and planning to get close to the truth about the underground conditions. Mostly the number and type of samples will determine the cost of this phase. For a site involving the possibility of hazardous chemical substances, standard tests are performed on samples of materials taken from the site by the assessor using standard techniques based mostly on experience. The costs associated with assessing a site usually include some clean-up and/ or repair costs:
Sample locations are determined by the assessor sometimes in consultation with geologial experts or state officials. Depending on the nature of a suspected hazard, protective clothing or other precautions may be advised. Excavation by heavy equipment may require special shoring or other structural precautions, expert excavating skills, or even professional structural consultation. Subsurface soil borings and sometimes groundwater monitoring wells are required if evidence points to a dynamic condition such as a past release of a hazardous substance underground. Some lenders and their underwriters may automatically require invasive testing of sites with known problems such as gas stations and certain maintenance and manufacturing facilities. Complicated sites may require official clearance by several agencies based on written proposals before excavation and sampling can begin. Every site is different. As a warning, sites involving strict oversight by government officials could exponentially expand site costs and result in delays and second guessing. Poorly qualified people sometimes inhabit positions of authority, and they may intercede in the management of a cleanup site unexpectedly trying to appear protective of the public trust. On the other side, site management can be mishandled. Misguided or inexperienced attempts to save costs such as avoiding getting permits or a qualified cleanup report can backfire. Pushing ahead with excavation can result in a serious mess if there is contamination found when a neighbor's complaint has brought on an official look-see. We handle sites under work suspension and with all sorts of complications. Fortunately, cleanup and assessment projects more often involve private consultants like us taking logical steps and solving problems as they arise. When to call for guidance from state officials, and when sharing information is necessary is clearly indicated with specific triggers and thresholds in state rules and guidelines. 2. Handling the samples: Samples must be taken from the site conforming mostly to strict protocols from the lab often determined through state rules. All samples must be numbered and carefully packed and conveyed to the lab under "chain of custody." When the cooler is passed from the sampler to the courier to the lab, signatures are required with dates and times for each handler. Once the lab has analyzed the samples, further rounds of sampling may be indicated to follow "hot" spots or chase substances down into the deeper soil layers. 3. Lab costs: Every chemical or biological material being tested will cost so-much per sample. For instance each standard soil and water sample checking for constituents of petroleum will cost $60 to $120 or more, sometimes based on the total number of samples handled. Samples have special storage conditions depending on the analysis. Some samples will have to be stored on ice for instance. Certain preservatives are required for some substances. Certain cleaned standard containers with special lids and labels may be required by the lab. A normal assessment for a small site seldom requires less than a dozen samples. Shipping, special sampling tools, and waste disposal can add to this cost. 4. Documenting the site work and interpreting lab results: Writing the report includes measurements, maps, sample locations and background data concerning the site and often its history. Three dimensional grids, computer aided drawings and many photos will likely be required to chronicle the process of the extractions. Investigative waste dirt with suspected contaminants will have to be placed on plastic or in drums awaiting transportation to a disposal facility once lab results are in. Interim reports may be required for each stage of sampling and a final report will be required when all the lab results are published. The final report must be complete with all technical results, but the report should be understandable by the average person. The report will likely be forever associated with the property. If public property is associated, the report may be officially recorded as a public document. 5. Getting rid of the waste: Each round of sampling is followed by lab testing until all samples fall below cleanup levels for the known substance. The total amount of dirt removed to the staging area is estimated and the concentration of the known hazardous material in the dirt is determined by lab results from several grab samples. The assessor will then search for the closest disposal facility. Some substances may have to be sent to regional incinerators or land fills in other states. Each disposal facility will have a cost per volume to dispose of each substance and the assessor will chose the cheapest often based on transportation costs. The site will then be backfilled with clean fill and surface improvements repaired and landscaped. The waste disposal facility will generally require a copy of the assessment report to determine the volume of the cleanup and investigative waste material and the concentration of contaminants usually based on a patern of grab samples. The Site Manager will usually be responsible to apply for the disposal application and fill out a profile document for approval by the waste facility. The Manager will also aquire hauling tickets to confirm disposal. Then a final report will be written to present to clients and possibly members of a cleanup team often including regulators. Then what? Following the final round of testing and report publication, the assessor will petition the state for a "no further action letter." There may be a waiting period specified to give time for additional problems or comments to immerge. Inspection ports or groundwater wells may be required for continual monitoring particularly if groundwater is involved. Other remedial action may be advised in the future. Otherwise the state may let you go at this point and the Level 2 environmental site assessment is complete. However If all of the hot spots were not followed down, if the contamination remains under buildings, or if all of the problem substance was not removed, a Level 3 Cleanup or a stabilizing cap or other construction would be the next step. If the sampling plan was logically laid out and accurately executed by qualified people, you will find the shortest path to peace of mind with your property, the eco-nomic solution. Conclusions: Because the prior existence of a hazard on property will affect the current value, everything possible must be done to contain and control problems when they are found. Careful checking may find no hazard or a simple cleanup. Success no further action is usually the result of thoughtful planning and intelligent action. Government agencies will generally stay out of a properly run site except to spot check and advise. ECO-NOMIC has the experience and is equipped to handle level 1, 2 and 3 sites primarily in Eastern Washington State. home level 1 or phase 1 environmental site assessment eco-nomic's facebook page Last Revised: 12/17/2016
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