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Joe Derhake Joe Derhake, President of Partner Engineering and Science, is actively surveying lenders, consultants, and environmental attorneys to better understand critical risk tolerance questions for lenders and real estate investors. This blog will address questions such as: What is a Recognized Environmental Conditions? How do lenders measure environmental risk? And after a REC is identified, what risk mitigation techniques are employed by lenders? |

Maybe my wife should have written this one—or maybe she would have advised young people to not…better to marry a doctor.
More seriously, how do consulting firms love their environmental professionals? When you run an environmental due diligence firm, you have to be good at it if you want to succeed.

This blog is a re-post. Math is the same, but I corrected a typo and I added some clarifications (see italics).
What do you do when you have groundwater sampling that shows solvent contamination and you want to infer a soil gas concentration, but you don't have soil gas testing data? This situation comes up a lot.
Maybe you are doing a Phase I ESA and know that the property across the street has high solvent concentrations in groundwater – hence the question, what are the highest soil gas concentrations that could partition from the saturated zone to the vadose zone?
Predicting the relationship between soil gas concentrations and groundwater concentrations is relatively easy in a controlled environment. You can use Henry's Law, which is a ratio of the concentration of a substance in air to its concentration in water. Of course, you can only go so far in the open environment of vadose zone soils with differing temperatures and pressures, etc.; but it is helpful to make a couple of assumptions to predict a range of reasonable soil gas concentrations.

When doing environmental due diligence in support of an acquisition, we are a small but sometimes very important part of a larger process. While our fee is modest, we are often supporting a very high dollar transaction. Occasionally we find ourselves center stage at the negotiating table. Maybe our Phase I ESA found a REC and we are asked to deliver an opinion that may kill a deal and cost several stakeholders a substantial financial loss. Sometime we find one of our peers/competitors across the table offering an opinion different than our own.
Situations like this, where we are put to the test, are when we really earn our money.
Our clients are generally graceful and diplomatic when negotiating with the other side. Real estate professionals understand the importance of relationships and future reputation. I have benefitted from the advice of some of the best in the real estate profession. "Be measured, but firm." "Be hard on the issues and soft on the people.” "Listen before you talk.”
I think clients respect when two engineers agree on the science, but differ as we get to risk tolerance opinion. Two environmental professionals pitted against each other can fulfill their respective missions gracefully and diplomatically by keeping the debate in a professional place. To do this I think you need to allow the other side to have their own opinion and to look for differences in the data analyzed.
When environmental professionals act as graceful and diplomatic extensions of their clients, they deliver quality environmental consulting service.

Much energy has been expended in this community in bemoaning the low prices of Phase I Environmental Site Assessments. No doubt we have seen prices drop during the great recession. Much of my practice is spent working for clients who are price sensitive, but I also have as many clients that are more concerned about quality!

Anyone in the practice of Phase 1 ESAs knows this story. A client calls and has two properties that need a Phase 1 ESA, but they are very close to each other. To save money the client asks to do the two assets as one Phase 1 ESA.
So where do we draw the line?
Clearly properties immediately adjacent can be lumped into one report; although if they have nothing to do with each other operationally, this lumping can make the report read awkwardly.
What about if the second property is directly across the street? What if it is non-adjacent but 300 feet away? What if it is a quarter mile away? Where is the limit?
If the two assets are not immediately adjacent, it becomes more difficult to deal with in terms of aerials and database reports. At some point the environmental consultant might be forced to order two EDR packages.
When the assets are not operationally connected, the report reads strangely. The consultant starts talking about property A and property B and they might as well just right two reports. I recommend doing two Phase 1 ESAs when assets are non-adjacent or not operationally connected.
I wonder if the ASTM E1527 standard can provide some limits here to protect consultants from having to write clumsy reports.

At this year’s EDR Client Summit I was asked to be part of a panel on Vapor Encroachment Conditions. The panelists were given case studies where a Phase 1 Environmental Site Assessment had been completed and the assessor had classified a condition as a Vapor Encroachment Condition. The panelists were asked to opine on whether or not these conditions were Recognized Environmental Conditions (RECs). The two cases were as follows:
A former dry cleaner has been identified from historical research in a shopping center located cross-gradient across the street, approximately 100 feet from the target property boundary. No data is available on the dry cleaner and the Phase I consultant identifies the dry cleaner as creating a VEC on the target property. Subsurface soil is sandy with some gravel. For more than 50 years, the target property has had a tall office building centrally located on it surrounded on all sides by open air parking and streets. The asphalt parking lot extends approximately 200 feet from the building to the road on all sides.
A state hazardous waste site with chlorinated solvents is located 1,000 feet up-gradient from the target property boundary. The source of contamination has been excavated and removed. Residual contamination remains in the groundwater with the contaminated plume approximately 920 feet long. A hotel is built on the target property approximately 100 feet from the boundary facing the hazardous waste site. The consultant defined this situation as creating a VEC on the target property.
The panelist generally agreed on the importance of considering the target property and the off-site concern as a specific location in space and not a “star” on the map. We also agreed that the client risk tolerance was an important consideration.
I raised a technical issue that related specifically to the definition of a recognized environmental condition and the de minimis exclusion. Below is the definition of a recognized environmental condition.
3.2.74 recognized environmental conditions—the presence or likely presence of any hazardous substances or petroleum products on a property under conditions that indicate an existing release, a past release, or a material threat of a release of any hazardous substances or petroleum products into structures on the property or into the ground, ground water, or surface water of the property. The term includes hazardous substances or petroleum products even under conditions in compliance with laws. The term is not intended to include de minimis conditions that generally do not present a threat to human health or the environment and that generally would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies. Conditions determined to be de minimis are not recognized environmental conditions.
For a vapor encroachment condition to be considered a REC it must not fall within the definition of a de minimis condition. If the VEC is neither a health concern nor a regulatory concern, then it is easily defined as de minimis.
“…conditions that generally do not present a threat to human health…”
If a vapor encroachment condition represents a threat to human health either for the current use or for a planned use of the property, then the environmental professional should classify the VEC as a recognized environmental condition.
“…would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies.”
This was the most interesting part of the panel discussion as ASTM is a little vague. I interpret this section to mean “would the owner of the target property be subject to a regulatory enforcement action”; as opposed to “would the owner of the off-site property be subject to enforcement action.” This is a huge distinction, as the target property owner is very rarely subject to enforcement action for an off-site release.
Someone in the room debated this subject with me. My argument back was that you do not consider the countless LUST, CERCLIS, and NPL sites in the surrounding areas to all be RECs, right? Why not? These sites are all subject to regulatory enforcement action. We don’t consider every nearby release site a REC simply because the owner of the off-site property is subject to a regulatory enforcement action (without other reason to believe that the off-site release has impacted the subject property or presents a human health risk to the subject property occupants).
In the end, I think that ASTM E1527’s definition of a recognized environmental condition could be clarified on this point.
If more than 99% of VECs do not meet the regulatory enforcement portion of the de minimis standard, then the much larger concern for a VEC to be a REC is whether it represents a human health concern.
There were clients at the conference that expressed greater sensitivity on this issue. To address these needs, the Phase 1 ESA consultants should fully discuss the vapor encroachment condition and if it does not meet the definition of REC, still include the discussion as an environmental issue (or some classification of elevated risk that is less than a REC).
In conclusion, the focus of the off-site vapor migration investigations should be on vapor intrusion conditions (vapor potentially inside a building, not just at the property line) and the corresponding threat to human health.

First, what does the term Expected Environmental Loss mean? It is a term I coined and introduced on my previous blog post. In short, it is the mean or expected loss that an owner will experience if they own a given asset with an associated recognized environmental condition. The term Expected Environmental Loss (EEL) is mathematically patterned after the Probable Maximum Loss product.
A series of Loss Scenarios could be imagined and then either through real data or professional estimates, a likelihood could be assigned to each scenario. Of course, each scenario is unique. Comparing the liability associated with a 20-year-dry-cleaner in California when groundwater is at 20 feet below ground surface with the liability of a 5-year-dry-cleaner in Colorado where the groundwater is at 100 feet below ground surface. However, large site-specific case variability does not stop us from opining on PMLs, so why should it stop us from opining on the Expected Environmental Loss?
So what is the Expected Environmental Loss on a Vapor Encroachment Condition? First, let me state that I don’t want to get too far into the debate as to whether a VEC is a Recognized Environmental Condition (REC) – VECs are often RECs but it depends on the site.
Secondly, my argument in past blogs has been that off-site releases rarely result in a big dollar amount for the owner of a site, if none of the following are true: 1) she is developing or dewatering the property; 2) the subject site has a drinking water well on-site; 3) the subject site has also released some sort of chemical and there has been co-mingling; 4) VOCs migrate on-site and represent a VEC.
Now, let’s take the 4th scenario where an off-site VEC would be considered a REC as the basic case study for this EEL:
A firm does a Phase 1 Environmental Site Assessment and finds that a retail center with no on-site RECs and on city water is 100 feet from a dry cleaner with a substantial release of PERC. After a file review of the off-site dry cleaner’s regulatory file, the EP concludes that PCE vapors likely have migrated to the site at soil vapor levels above human health screening levels (HHSLs). Since vapor levels are likely above the HHSLs, the EP designates the Vapor Encroachment Condition a REC.
Here is my EEL estimate on this VEC/REC case. Suppose that I have had 100 clients in this exact situation. Let’s say that all 100 clients purchase the property anyway and owned the office building for the next 20 years. Here is my supposition on the resulting scenario likelihood:
50 Office Buildings Zero Loss
29 Office Buildings Minor Loss; forced to do Phase IIs during financing. $10,000
20 Office Buildings Does an investigation, a risk assessment, installs a venting system. $40,000.
1 Office Building Conducts active remediation on the on-site fraction of the plume. $100,000
Total Loss = (50x$0) + (29x$10,000) + (20x$40,000) + (1x$100,000) = $1,190,000
EEL = Total Loss/Sample Size = 1,190,000 /100 = $11,900.
If we look at the past 10 years, I think loss rates on this issue are far lower than the above estimates. However, the EEL is intended to be forward looking.
I think someone could argue that as awareness of these issue rises the third category will grow, but even so I don’t think that the EEL is going to get larger than $25,000.
Some might argue that this data is all made up and arbitrary. Well, that is how predicting the future goes. We must use the best data and experience we have, and extrapolate that to estimate what the future might look like. VEC loss data from the 1990s would not be very meaningful. If our client is a buyer, she needs to know what the next 10 or 20 years will hold in liability.
The REC represented by a VEC from an off-site source is a soft REC compared to that of an on-site gas station. The difference between EELs of an off-site VEC, $11,900, and a gas station, $164,000, is huge. See my previous blog on Expected Environmental Loss for a discussion of the gas station EEL.
I wonder if some users would be willing to post their view on how such a data set would look in the future. What do you think?

If I own 100 gas stations for 20 years, what is my Expected Environmental Loss (EEL)?
For an environmental consultant to provide some sort of measure of “expected” environmental risk and related financial loss, as opposed to the worst-case risk, is extremely valuable to real estate investors. Real estate investors constantly balance risk and reward. The environmental consultant tends to speak in worst-case-scenarios. Our clients need the worst-case-scenario, but would also greatly benefit from the most-likely-scenario—or the EEL.
Data exists to provide pretty good estimates, right? There is tons of data out there. For the gas station scenario, we could grab data from 1,000 State UST Fund Sites, add up the expenditure and divide by 1,000. I have been told by the California UST Fund that the result is $167,000. Can we call that the EEL?
One could argue that by definition these sites are sites with releases, so the derived EEL would be skewed too high, or that releases in the future should be less common and smaller than the past. Fair arguments, but I would argue that some quantitative measure is better than none.
Let me layout my definition of the EEL—I recently coined this term. The EEL is all potential environmental costs, multiplied by the percent likelihood of that scenario coming to pass. Here is an example of how to calculate it:
Let’s use the following site as a make-believe case study. A property was used as a gas station for the past 20 years, with no Phase II data, in a given state. In that state, we were provided the following loss data from a major oil company on 100 sites that they owned in this state:
30 Gas Stations: Zero Loss
30 Gas Stations: Minor Leak. Average loss for this bucket is $80,000
30 Gas Stations: Substantial Leak. Average loss for this bucket is $200,000
10 Gas Stations: Huge release. Big plume. Average Loss for this bucket is $800,000
Total Loss = (30x$0) + (30x$80,000) + (30x$200,000) + (10x$1,400,000) = $16,400,000
EEL = Total Loss/Sample Size =16,400,000 /100 = $164,000.
Realize that this math is on a make believe data set, but I think that we as an industry could do a few studies and define this word.
Now if you are working in this make believe state on the gas station with no existing subsurface data, you could site that the Average EEL for gas stations in this state is $164,000. Then just like structural engineers adjust PMLs for unique characteristics, the environmental professional could adjust the EEL up or down based on site specific data, such as groundwater, soil type, or proximity to sensitive receptors. The end result would be a bit inexact for sure, but would give clients a great order of magnitude appreciation of risk.
Gas stations often represent a bona fide recognized environmental condition, but consider how the data set looks for a much softer REC. For example, how might the buckets look if we are talking about a hydraulic lift? This data is harder to find, but any of us who have been in the business for 20 years might be able to offer a good guess or even a valuable data set. Just for fun let’s speculate what that example looks like:
Assume a guy owns 100 sites with 3 hydraulic lifts on each site. Assume for simplicity that he did not use other chemicals in the course of his business. I am guessing the data set would look like this:
50 Sites: Zero Loss
20 Gas Stations: Minor Leak. Average loss for this bucket is $5,000.
20 Gas Stations: Substantial Leak. Average loss for this bucket is $20,000
10 Gas Stations: Huge release. Big plume. Average Loss for this bucket is $100,000
Total Loss = (50x$0) + (20x$5,000) + (20x$20,000) + (10x$100,000) = $1,500,000
EEL = Total Loss/Sample Size =$1,500,000 /100 = $15,000.
So if I had these data sets available, I could give my clients far more quantitative advice that the binary REC / no-REC advice.
I would tell the gas station-buying client that the EEL is $164,000 and that the reasonable worst case scenario is $1,400,000.
I would tell the hydraulic lift-buying client that the EEL is $15,000 and the reasonable worst case scenario is $100,000.
I’m curious what other consultants think. Has anyone developed this type of data?

My mission statement came from a conversation with my father. My father was 5 years retired and he was reflecting on his career. He was an automotive engineer for Cadillac and Buick. He had a fine career getting promoted up the ladder as an engineer and as an executive. When I asked him what was the most meaningful achievements in his career, he said: “the people”.
I was surprised by this answer. Car companies produce cool products….or at least a lot cooler than a Phase I Environmental Site Assessment. I asked him: what about the cars? He said no, it was the people that he managed, mentored, and worked alongside. Hmmm?
It is normal to compare yourself to your father and as a civil engineer doing Phase I ESAs and PCAs, I always felt like less of an engineer than a man who designed cars. True as this may be, I found an opportunity to be successful in the arena that my father thought most important: the people!
I set out to do something great: build the best firm for talented employees. I have more control over the work environment in my consulting firm than my father did at GM, and this has been our mission from day one.
I even kicked around a tagline of “Clients 2nd, Employees 1st!” I think sophisticated clients would realize that happy, talented employees yield good service and high quality.
Values are critical to attracting and retaining quality professionals. A company must stand for something other than making money. Staying true to values, even when difficult, has helped us create an environment where people work together and like each other. We spend too much of our life at work to not get along with the people on your own team. In the end, we might struggle to tell our grandchildren why our work was so important – we might end up like my father and talk about the PEOPLE.

Characterizing an off-site release as a Recognized Environmental Condition during a Phase 1 Environmental Site Assessment (ESA) has never sat well with me simply because in 19 years of practice I have yet to do a major environmental cleanup where a regulator was forcing a totally innocent property owner to cleanup his neighbor’s mess.
Now I have had a dozen or more instances where a client has experienced expense as a result of the neighbor’s release. These instances fall into five categories:
While the five scenarios presented above are all serious, we can often eliminate 4 of these quickly: often the client does not plan to develop, there is no reason to suspect an on-site release, there is no on-site dewatering system, and drinking wells are usually deep enough to avoid impact from off-site contamination (provided you can document the well depth and have good information regarding the extent and migration of the off-site plume).
That leaves Vapor Encroachment as the primary reason to consider an off-site release a Recognized Environmental Condition in a Phase 1 Environmental Site Assessment. A large up-gradient release can migrate in vapor phase or through ground water and create a vapor intrusion condition. Vapors can migrate up from groundwater, through the soil column, and into the subject property building. After 15 years of soil vapor sampling this phenomena is well proven and not all that uncommon.
What is uncommon is a real estate owner being forced to write big checks on account of this condition. First, most real estate owners are not that proactive when it comes to vapor encroachment. Second, vapor encroachment conditions can often be mitigated relatively affordably—at least compared to soil and groundwater remediation. I agree that a vapor encroachment condition is a recognized environmental condition; however, these off-site issues are certainly a lesser concern than an on-site issue.

On February 8th, 2011, the city of San Francisco adopted the San Francisco Existing Commercial Building Energy Performance Ordinance, requiring owners of non-residential buildings in San Francisco to obtain energy efficiency audits, as well as to measure and disclose energy performance annually.
The owner of every non-residential building in the city of San Francisco shall annually file with the Department of the Environment an Annual Energy Benchmark Summary report (AEBS) for each covered building using ENERGY STAR® Portfolio Manager. The AEBS shall be based on assessment in Portfolio Manager of the entire non-residential building and related facilities and must use 12 continuous months of data ending no earlier than two months prior to submittal to the Department of the Environment.
Annual Energy Benchmark Summary reports from Portfolio Manager shall be filed with the Department of the Environment according to the following schedule:
The owner of any non-residential building with a gross area of 5,000 square feet or greater shall conduct a comprehensive energy audit for each such building not less than once every five (5) years. The energy efficiency audit shall meet or exceed standards set forth by the American Society of Heating, Refrigerating, and Air-conditioning Engineers (ASHRAE) Procedures for Commercial Building Energy Audits (2004).
The energy professional performing or supervising the energy efficiency audit must have one of the following qualifications:
The owner of every non-residential building shall file a Confirmation of Energy Efficiency Audit for each covered building with the Department of the Environment. The Department of the Environment shall establish a schedule such that:
Buildings owners may comply with the first assigned due date for an energy efficiency audit by submitting records of audits, retro-commissioning, and retrofits performed not more than three (3) years prior to the effective date of this ordinance.
The new San Francisco Existing Commercial Building Energy Performance Ordinance will force building owners to benchmark their buildings via EPA's Energy Star, which they really need to anyway to comply with Califronia Energy Disclosure Law AB 1103. AB 1103 requires property owners to disclose their buildings Energy Star Portfolio Manager ratings during lease, sale, and financing transactions. So on some level, building owners were required to do their energy benchmarking work anyway.
2011 should be an interesting year. Email me if you have further if you have further quesiton: joe@partneresi.com.

I had the good fortune of moderating a panel at the Environmental Bankers Association (EBA) January Conference on the subject of QA/QC of Phase I Environmental Site Assessments and the entire environmental management process during underwriting.
The premise of the panel was to study error in order to make future environmental due diligence better. Senior credit officers are asking the environmental risk managers: How did this REC site slip through the cracks (or did it)? Why are we having to do Phase II Environmental Testing on fully underwritten loans?

The commercial mortgaged-backed security (CMBS) industry has been reborn in 2010. CMBS underwriters call their new underwriting paradigm CMBS 2.0. Providers of third party reports such as Phase I Environmental Site Assessments, Property Condition Assessments and Probable Maximum Loss reports ask: What does CMBS 2.0 mean to our trade?
The Phase I Environmental Site Assessment and the Property Condition Assessment are rather standardized and in my opinion are being provided to CMBS lenders with great reliability. The Probable Maximum Loss report needs standardizing. In 2007, ASTM published two new standards for Probable Maximum Loss Reports: ASTM E2026-07 Standard Guide for Seismic Risk Assessment of Buildings, and ASTM E2557 Standard Practice for Probable Maximum Loss (PML) Evaluations for Earthquake Due-Diligence Assessments.
These new ASTM Standards improve the process, but are too flexible. For example, the standards do NOT specify how an engineer should calculate a PML and some engineers perform calculations that are out of the mainstream or worse, do no math at all—they just call it based on their judgment. Of course my colleagues may be very good engineers, but what the industry needs is an objective measurement of seismic risk. The process should be transparent and peer reviewable.
Objective reliable Probable Maximum Loss Reports are easily achievable; we just need some help from our clients. Yes, the clients must do their part. If clients require the following we will be more than half the way there:
1) Only order reports from firms with registered engineers on staff;
2) Require the engineer to show his/her math;
3) Require that the engineer call the Scenario Expected Limit as the PML, but also report the Scenario Upper Limit.
I have participated in writing the Probable Maximum Loss Scope of Work for several lenders and my rational for my recommendations is presented more thoroughly in my RMA Journal article titled Managing Seismic.
Happy Holidays,
Joe Derhake, PE

Environmental consulting is a fine field for entrepreneurship; in fact that is how I ended up in this field.
In college I did internships with Texas Instruments and a medium-sized environmental consulting firm. Upon graduation I turned down an offer to work as an engineer in Texas Instrument’s semiconductor division for a job as a staff engineer with PSI, because I thought that the environmental consulting field offered great entrepreneurial opportunities. Of course, there may have been a few opportunities in the field of information technologies—what can I say I was 22 years old.
Change creates opportunity. Changes in laws, the economy, or technology can create new opportunities for entrepreneurs. Ability to adapt to change is the entrepreneur’s advantage over big companies.
What is intrapreneurship? Intrapreneurship is simply entrepreneurship within a larger company. While that may seem like an oxymoron, if the company is structured right it is possible and my company, Partner Engineering and Science, is proof.
In my view, three important elements of intrapreneurship are:
Control: Obviously the entrepreneur must have a strong degree of control over their business within a business. This requires a good relationship with the company’s management and a management structure that is not prone to micromanagement.
Equity: Creating something of value is difficult. If the entrepreneur is going to do this within a company instead for themselves, they must believe that they can ultimately realize the value that they create. Beware of phantom equity. Ultimately the entrepreneur must have some solid contractual rights.
Platform: If the entrepreneur decides to create within a company instead of on her own, then she must get something in return. The company must bring a lot to the table and the company must be good at these functions. A few things that the company can contribute are: capital, technology, brand, a sales force, and common corporate functions (HR, IT, accounting etc…).
If you want to be an entrepreneur, go for it! If you are in a position in life that does not allow you to take a lot of risk, consider sharing the risk with a Partner. Intrapreneurship might be for you.

The SBA published their latest update their environmental policy in SOP 50 10 5 (C). The SOP revisions take effect on October 1st, 2010 we should all bone up on a few of the new elements of SOP 5010 5 (C) (pages 199 – 206 & 310 – 317).
One now technical but important point is that the Reliance Letter has had a revision and the Reliance Letter from SOP 5010 5 (B) will no longer be accepted by the SBA. Lenders should make sure their environmental consultant knows of the new Reliance Letter before ordering an SBA Phase I Environmental Site Assessment.
Overall the Environmental Requirement changes in this latest SOP were minor and summarized below.
Much of the information in this Phase 1 Environmental Site Assessment blog was provided by my partner, Gary Reynolds, our SBA Expert.
| type | name | rating | author | activity | ||
|---|---|---|---|---|---|---|
| Entry | Human Health and Soil Vapor | 0 | 1398 | JoeDerhake![]() | - never | |
| Entry | Passive Soil Venting Systems: when are they appropriate? | 0 | 821 | JoeDerhake![]() | December 9, 2009 | |
| Entry | Groundwater vs. Ground Water | 0 | 813 | JoeDerhake![]() | - never | |
| Entry | Phase II Design: Test Soil or Soil Vapor | 0 | 758 | JoeDerhake![]() | - never | |
| Entry | Summary of the SBA's SOP Environmental Policy Revisions... | 0 | 678 | JoeDerhake![]() | September 11, 2010 | |
| Entry | Building Energy Performance Disclosure | 3.0 | 0 | 569 | JoeDerhake![]() | May 26, 2009 |
| Entry | Expected Environmental Loss on a VEC | 0 | 502 | JoeDerhake![]() | May 13, 2011 | |
| Entry | Risk Classification: Standard Practices? | 0 | 460 | JoeDerhake![]() | - never | |
| Entry | San Francisco Commercial Energy Performance Disclosure and... | 5.0 | 0 | 428 | JoeDerhake![]() | February 13, 2011 |
| Entry | TCE by Another Name would Smell as Putrid | 0 | 361 | JoeDerhake![]() | March 29, 2010 |
| type | name | rating | author | activity | ||
|---|---|---|---|---|---|---|
| Entry | How to Love an Environmental Professional | 2 | 376 | JoeDerhake![]() | January 8, 2012 | |
| Entry | The $5,000 Phase I Environmental Site Assessment | 4.0 | 22 | 1869 | JoeDerhake![]() | September 6, 2011 |
| Entry | Phase 1 ESAs on Nearby Assets: One ESA or Two? | 14 | 534 | JoeDerhake![]() | August 5, 2011 | |
| Entry | Off-Site VEC and De Minimis Environmental Conditions | 9 | 950 | JoeDerhake![]() | June 17, 2011 | |
| Entry | Expected Environmental Loss | 5.0 | 4 | 842 | JoeDerhake![]() | April 28, 2011 |
| Entry | Mission Critical: It's All About the People | 2 | 822 | JoeDerhake![]() | April 20, 2011 | |
| Entry | Off-Site Recognized Environmental Conditions (RECs) | 9 | 1156 | JoeDerhake![]() | April 6, 2011 | |
| Entry | Quality Control / Quality Assurance – Phase I E... | 6 | 837 | JoeDerhake![]() | February 2, 2011 | |
| Entry | Probable Maximum Loss (PML) Scope of Work for CMBS... | 3 | 733 | JoeDerhake![]() | December 16, 2010 | |
| Entry | Phase I Environmental Site Assessment Risk Decisions | 2 | 895 | JoeDerhake![]() | July 30, 2010 |
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