The Fracking Conundrum: What to do?

The Fracking Conundrum: What to do?

 



Restored oil well area in Alberta. There is no significant difference with the surrounding land use

 

Like almost all human activities, fracking is neither good nor bad and is strongly influenced by local conditions and culture.

 

Two years ago, I wrote about the analysis of hydraulic fracturing, finding two types of results. On the one hand, hydraulic fracturing accumulates many scientific, technological, administrative and financial advances. And on the other hand, fracking presents a very negative public image, especially in American and European countries, with a significant emotional charge. Contrary to what I expected, the most developed and educated citizens show considerable opposition. When studying the subject, I found that a large part of the impacts, except one, are understood and regulated in the vast majority of countries. That is the relatively new point of induced seismicity. Everything else is controlled in one way or another in most countries or recommended by the oil industry associations.

When I was writing the original articles, I expected to get questions and comments of all kinds. Still, I received many environmental scoldings and very few questions from interested people. I believe that all the fauna of "Trolls" and other beings of the electronic underworld manifested while environmental and oil professionals remained absent.

I decided to wait a prudent time for the passing of the months to decant things. I returned to the topic at the end of 2021 with the expectation of finding changes.

I explored the most recent articles and postings on the Internet. A Google query with the term "fracking" returns about 29 million entries on the network. I analyzed 71 articles, journalism stories, and long documents to identify people and industry concerns about fracking. I found a significant repetition of the initial arguments and little change in the recent ones.

By the end of 2021, I found that a more significant number of websites opposed fracking and even an international society with permanent staff collecting money to campaign against hydrofracturing. On the other hand, the explanations of hydraulic fracturing in oil industry associations and environmental authorities are a little more complete but still far from containing the information that the public asks for. In many cases, they show simplifications and drawings so schematic that they intuitively generate doubts [1]. The videos are short. In general, there is no clear presentation of the fracking activity, nor of the people who work in them. Also, the few explanations and videos do not present the complexity and risks for industrialists or the public.

The revised Internet documents present almost the same complaints as in previous years. Many documents repeat what has already been expressed and with vague generalizations. The vast majority of journalists in the traditional media draw attention to unverified aspects. In general, people request things contained in regulation and environmental studies. Still, how people express their concerns, complaints, and emotions does not allow good communication between authorities, design engineers, investors, and the public. Any analyst studying fracking can find examples of distrust and manipulations (conspiracies) in almost every actor except in design engineering firms. Regrettably, it can be said that several of the actors do conspire. Managing and solving this situation is complex and requires the support of the companies, oil industrial unions and the local government.

Complaints from both the public and the industry reveal ignorance of the regulations and obligations of the parties. Attentive and clear communication tends to be minor. Ignorance of commitments and rules activates distress behaviours in the public that lead to emotional chaos in the hydrofracture practice.

There is a perceived feeling of talking to irrational interlocutors when speaking with environmentalists opposed to the industry. Also, industrials believe they are being restricted in their rights and ignoring their economic contribution, feelings that make them prone to disqualify "green" interlocutors. Most of the industrial authors of the revised documents do not fully understand the importance and use of environmental instruments and regulations. This industrial behaviour requires the participation of environmental psychologists, sociologists and social communicators.

Like almost all human activities, fracking is neither good nor bad and is strongly restricted by local conditions and culture.

To have a better ability to act in cases of hydrofracking, all parties must understand the effects, impacts and risks that hydraulic fracturing can generate and have a minimum common terminology.

To have solutions, each environmental professional and any interested person must have a broad mentality with explicit rationing, critical capacity, impartiality, and understand and use the "Right to Know." This right is typical of information-intensive democratic societies that use democracy and the market economy as essential instruments. Likewise, the stress generated by fracking on the local inhabitants must be respected since irresponsible generalizations create conditions of moral panic.

Rachel Carson's "Right to Know" (1962) empowers people by allowing them to participate in an informed manner in decisions that affect them and at the same time holds governments and entities accountable to participate in decision-making with the public. This right to know implies the "Clifford's Principle of Epistemic Responsibility" (1877), which says: "It is wrong always, everywhere and for anyone, to believe something with insufficient evidence" [2].

Democracy, open information societies and a market economy always go together (a topic of another article). On environmental issues, the concept of "Right to Know" was presented by Rachel Carson in her book Silent Spring [3] and is a central theme in democracies, open information societies, market economies and environmental regulations.

The most significant difficulty in understanding the public's position is their lack of knowledge of each of the necessary steps of the hydrofracture projects. An ignored part for the people, and one that generates distrust, is how companies decide to start the hydrofracture drilling process to extract the resources contained in the geological strata. Few of the opponents know that once the Feasibility Studies of the hydrofracture are initiated, environmental studies and communication with the authorities, the community, and the landowners are also started. The public is unaware that the main permits are obtained in the feasibility phase. Later, the investors decide to invest when the main permits are assured. Once the decision to invest is taken, the local and other minor licenses are acquired during the design phase. Usually, the public realizes that the project is a reality and the timing to expose their views is generally late for the authorities and the project.

Nevertheless, locals and other stakeholders can participate in all these stages. In most countries, participation is mandatory, and designers follow strict protocols to communicate projects to the population. But once a major licence is conceded, it isn't easy to reverse the decision.

The interaction between the public, owners and designer engineers is not easy. A project gets "frozen" in many situations because the population opposes it. The oppositions are in part because:

a)     the local people have no good experience in democratic processes; and,

b)     the innate human tendency to maintain the status quo; and,

c)      the above points are combined with the desire to "make feel our presence or existence," especially in cases of marginalization.

Hence the importance of social psychologists and environmental sociologists in the hydrofracture projects.

In the population with experience in democratic processes of consultation and voting, the emphasis shifts to personal and community opportunities and disadvantages. This experience can lead to long times of tension and negotiation. In this process, negative perceptions of the oil industry and fracking weigh heavily on community decisions. Typically, design engineering firms adjust the project to comply with all laws and be accepted by local communities, but not always.

It is common for the public and local authorities to ignore that project owners instruct their design engineers to "design the project to be approved and attract investors," but this is only possible if the cost/benefit balance allows it. In this sense, the "surface environment" weighs heavily in the cost-benefit balances and is perceived as a burden by the owners. At the same time, the value of the extracted material compensates for the costs of the "underground environment." This dichotomy is a false perception.

Agreements are usually reached between the community, the government and investors. However, a noisy minority can bring down an entire process, and political instability or an outbreak of violence can scare away investors.

In my experience, discussions between design engineers, project owners, government and the local community move from readings, analysis, and explanations of impact studies with their complex methodologies, to talks about avoiding, reducing-mitigating, and compensating impacts. The agreed actions will be expressed in action plans and monitoring plans. The public wants to know the central point of how each impact is reduced-mitigated and compensated. Hence the importance of concrete management plans, specific to the issues perceived as important, with their resources, compliance policies and assigned to the operating firm.

Below I present the most important observations that account for more than 80% of the complaints about the hydrofracture technique that the public makes. The documents, in my experience, clearly contain the answers that the public needs. The curious thing is that almost all the information necessary to complete the management plans is available during the phases of feasibility studies and designs, with few exceptions. Government institutions and public data already generate part of the required information. They are documents that can be prepared quickly by someone with experience in the subject.

Environmental professionals and interested persons should be aware of the main observations that the public has of fracking. These can be gathered into five categories. The recommendation on what should be prepared by engineering firms and what may be requested by the public are:

 

1- Effects resulting from the industrial activity itself,

a) Increased accident rate for the population. It is a natural consequence of the increase in activity in the areas where fracking occurs. To internalize the rise in local accidentality is the Health Impact Assessment". This Plan is designed and coordinated with the Emergency Prevention and Response Plan, the Water Monitoring Plan and the Air Quality Monitoring Plan, covering potential toxic pollutants. These studies and plans are public and almost always mandatory. The interested person can ask for them.

(b) Air pollution. It is an essential point of the EIA Environmental Impact Studies. The project's design considers the acceptable limits, and an Air Quality Monitoring Plan is established. The limits on particulate matter and gases are strict.

(c) Noise and vibration pollution. It is an essential point of the Environmental Impact Studies. The project's design considers the acceptable limits, and a Noise and Vibration Monitoring Plan is established. This Plan should include audible sounds, infrasounds (such as when feeling low notes such as drum vibration felt in the belly and diaphragm), ultrasounds (such as dog whistles), explosives, rhythmics or explosion waves, etc.

(d) Unpaid and uncompensated damage to local property and infrastructure. Curiously, this is a point that is not adequately identified in several environmental impact studies or the regulations of several countries. There are countries where these aspects are considered at the level of permits and authorizations to use roads, canals, public services of aqueducts and sewers, etc. A repeated complaint is damage to roads and bridges. Since the use of roads is a generally open access service in most countries, the compensation of damages is in the hands of local authorities, the infrastructure owners, or the authority that issues the road use permits. Other arguments are about water infrastructure and obtaining water from rivers, lagoons, wetlands, wells, dams, cisterns, etc. Several complaints are about the access to rivers or canals to dispose of water from the interior of the area and the delivery of flows from rainwater drainage and storms. In these cases, the definition of what to do is usually made in the Environmental Licenses. The designer shall submit complete studies and define an Infrastructure Adaptation Plan covering the project area to obtain water concessions and permits. To compensate for the environmental impact of traffic, it is customary to include improvement of specifications, traffic signs, protection of water infrastructures and others. To compensate for water management cases that may affect the capacity of drainage channels, natural drainage, rivers and wetlands or affect their quality, two plans are essential, the Erosion Control and Soil Protection Plan and the Storm Water Management Plan. The environmental authorities usually request those plans.

(e) Environmental, landscape, biodiversity and ecosystem services degradation. This aspect is one of the central points of the Environmental Impact Studies, and questions from the public reveal a severe failure of these studies; since one of the main points is to inform those affected of the possible effects and impacts, the plans to mitigate them and the indicators to monitor them. Each of the impacted aspects requires specific points in specific management plans. These have titles such as Plant Landscape (or Ecosystem)  Management Plan,  Vulnerable  (or Endangered) Animal and Plant Species Management Plan, Natural and Recovery Area Management Plan, Invasive and Undesirable Species Management Plan,  Management plan for poisonous, toxic and dangerous species, the Management plan for vector species important for human and animal health, the Biodiversity protection and management plan, etc.

(f) Oil spills and their consequences. Spills are one of the central points of the Emergency Prevention and Response Plan. In general, emergency management plans contain a series of chapters for environmental emergencies identified in the Environmental Risk Study. Keep in mind that the study of environmental risks is another of the central points of environmental impact studies. The risk study considers several possible leaks and spills (involuntary and unexpected discharges) of gases into the atmosphere and liquids and solids into soils and waters. The reader must be very clear about the potential damage multiplied by the possibility of occurrence and how the project owner takes the appropriate insurance policies to the emergency plan for all these incidents. All participants should be aware that there are entirely unacceptable incidents:

1.     loss of human life and damages to health,

2.     the change o reduction of vital resources to the population,

3.     the affectation of endangered species increasing risks of extinction,

4.     the destruction of essential habitats, and

5.     damage to ecosystems and their environmental services.

The Plan should contain alerts and alarms for the population and local authorities of the potential impact area estimated by modelling the events and the areas covered by the monitoring and follow-up of the status of the other environmental values.

(g) Permanent deterioration of the landscape and land use. This complaint stems from the absence or vagueness that some local or state authorities have about the importance of land use plans and reclamation plans. There are jurisdictions where the land ownership is total, and the owner owns absolute rights of the wedge that his property generates up to the planet's center. This complete ownership leads to land use problems and vicinity of activities by not considering the distance of retreat, visual effects and generalization of land value (the lousy house in the good neighbourhood lowering the price of the homes around). These two points require that the engineering designers follow in detail land ownership local regulations, the regional land-use planning and the requirement to comply with the Land Use Plan and take the Insurance on the complete restoration of the expected final use. The location of the works must respond to the land ownership rules and the regional land-use planning.

(h) Methane leaks. This aspect is part of the project's design and is quite regulated in most countries. Any interested person can request the presentation of the design and operation measures for handling gases, avoiding leakage, capturing gases from tanks, managing teas, gas incinerators and chimneys, etc. In most complaints, people don't know the differences between Natural Gas and Methane. Methane is a component of Natural Gas. The typical composition of Natural Gas is 95% methane, 4% ethane, and the remaining 1% is a mixture of propane, butane and isobutane. Sometimes it is not necessary to request a specific management plan but to know what type of management the company will give to recover natural gas, including methane. Monitoring for potential leaks and correct leaks is essential. In cases of considerable gas volumes, the design engineer must prepare a Plan for the recovery of natural gas and the combustion management in teas, torches, and gas incinerators. Those points are required in most countries. And in somewhat more extreme cases, it has to be complemented with a Plan for monitoring, control and management of natural gas leaks and other gases. What is essential is the burning of the H2S and the dispersion model of the SO2. All these aspects must be included in the Emergency Prevention and Response Plan. This emergency prevention is a critical plan, and it should be based on a detailed study of environmental risks.

e) Impact by heavy vehicle traffic. Apart from using road infrastructure, it is necessary to consider a plan for managing heavy traffic during the fracking process that uses large trucks and trailers intensively. Sharing the road infrastructure requires a Heavy Traffic Management Plan. It may contain the improvement of signage, the dates with heavy traffic and the precautions that neighbours must follow. This Plan is a "good neighbour" plan informing the need to occupy the road. This Plan requires courtesy to neighbours and local authorities. From experience, I know it is very uncomfortable to reverse a few kilometres to make way for a large vehicle.

f) Impact from the management of sludge and water from drilling. This aspect is a normal part of the management of oil drilling and is intensely regulated, except for a few countries that have not yet updated their regulations. In these cases, you should ask about the handling and destination. There is a detailed regulation for facilities treating drilling sludge and water. Dispatches of those waters follow detailed instructives, use transparent chains of custody and provide receipts. Usually, the designer presents a Sludge and Drilling Water Management Plan. In case of doubts or conflicts, the materials' tickets can be requested at the facilities for treatment and disposition.

g) Impact of the management of garbage and waste from oil exploitation. In this case, it is very similar to the previous one. The vast majority of countries require that firms treat waste materials from oil and gas exploitation at specialized facilities. Materials are collected and transported with clear tracking protocols or custody chains. Those protocols generally include treatment and final disposal. The designer must prepare a Plan to manage garbage and waste from the hydrofracture processes. As in the previous case, the interested stakeholder must request the documents of the custody chain and the receipt of materials at the disposition points

h) Use of large volume of water. This is one of the biggest complaints, especially in arid regions with water scarcity, competition for water use and a high water value. The overconsumption of water is a complicated perception to handle. On the one hand, the volume is insignificant compared to other agricultural or industrial practices. Still, each drilling requires a significant water volume for a small producer or the inhabitant of an area with a water deficit. All waters in all countries are subject to detailed regulations. The project designer must prepare a Hydro Fracture Water Management Plan respecting all local and national rules and fully consider local customs. The Hydrofracture Management plan should be presented at meetings with all local stakeholders.

 

2- Serious technology failures under specific well conditions

a) Blow-out. The blow-out of a well is a rare condition as the well is controlled with very high precision. Each well uses a variable amount of barium-rich material (called barite, which are barium sulphate clays (BaSO4)) to increase the weight of the sludge column to prevent a blow-out. The detailed well control is an operational detail of the project in charge of the drilling engineer; however, the blow-out control may be requested by local inhabitants or the authorities. The blow-up is part of the Emergency Prevention and Response Plan.

(b) Contamination of aquifers, surface waters and soils by hydrofracturing liquids. This contamination is the most common complaint and one of the most complex aspects to deal with between the parties due to fake news and manipulations. The ignorance of some environmentalists is regrettable, and that of the affected communities, in general, is very high. This subject reflects a failure of the social part of the project that has significant effects. One of the aspects opponents of hydrofracture ignore is the presence of five layers of insulation between geological strata and fracking wells. Most are unaware of the high technology of horizontal drilling, detailed knowledge of geophysical aspects, depth of reservoirs and handling of sludge and liquids during drilling. Countries have different approaches, but the vast majority prohibit mercury, lead, chromium, cadmium, arsenic and any radioactive elements. Also, most country regulations require the absence of carcinogens and compounds such as benzene, toluene and xylene (BTX) and their derivatives. But other countries, especially the USA, insist that the composition of hydro-fracture liquids is part of the technique's intellectual property, creating a conflict between the perceptions of private enterprise's right and the right to know. The behaviour that some citizens perceive as freedom is perceived by other citizens as bulling. And vice-versa, what is perceived by the second as irresponsible behaviour, the first ones perceived it as a right. In general, hydro-fracture drilling is used only in deep reservoirs, contained between mantles of impermeable rocks that limit the leakage of liquids into other formations. The central flow in wells is inside five different layers of protection. The probability of rupture is efficiently controlled as the costs of these wells are pretty high, and regulations for accidental spills have severe penalties. If the stakeholders have doubts, the designer engineers shall prepare an Emergency Prevention and Response Plan, the Hydro-Fracture Water Management Plan, the Sludge and Drilling Water Management Plan, the Health Impact Management Plan, and the chapter in which the Geophysical Study consider the geophysical aspects, and the Seismicity Risk Reduction Plan. Those plans and the chapter usually contain all the needed information for the hydrofracture contamination.

c) Exposure of the population to toxic chemicals by hydro-fracture liquids. These cases are very low probability given what is provided in the above numerals. But if someone has concerns, the engineering designers must prepare the Emergency Reduction and Response Plan, the Hydro Fracture Water Management Plan, the Sludge and Drilling Water Management Plan, the Health Impact Management Plan, and the Geophysical chapter with its conclusions.

 

3- Effects not previously contemplated

 a) Induced earthquakes. The induced seismicity is an issue that until 2019 was not regulated in most countries. It can be said that seismicity emerged to the public in the last five years. The problem comes to light with the earthquakes of the drilling zones in northern British Columbia, Canada and in the central United States. The first geophysical models were from 1998 when the issue was raised. By 2020 these models include confinement and minor local fault and micro fault systems. Due to the long experience with the technique in the reactivation of wells, the current hydrofracture studies include microfracture analysis as part of the mechanisms to support the extraction of gases and liquids, but not as the potential source of small earthquakes. The earthquakes are only perceptible by the inhabitants of nearby areas. Earthquakes originate by water facilitating the activation of micro faults and local faults, producing a local rearrangement of the stress of the geological mantle and adjacent ones. By its nature, seismicity is of low intensity unless a fault already subjected to stress is activated. Such faults are identified in the Geophysical Study and can be modelled with reasonable accuracy. The interested party can ask for the Geophysical Study and request a Plan to reduce and manage induced seismicity. Induced microseismicity can reach values of scale four on the Richter's scale and can be crucial in areas of high instability in mountainous regions. A chapter should be included in the Emergency Prevention and Response Plan if necessary.

 

4- Social effects of the project

a) Anxiety and distrust – "complete lack of trust" – This is an old-fashioned condition of complete lack of trust. It comes from the time of the Rockefellers, Mellons, Flaglers, Gates and others from the beginning of the oil industry when disinformation, manipulation and abuse of the position of power were valid tools to manage the market. Unfortunately, the entire industry adopted closed management and misinformation for the next 75 years. Things began to change around the 1980s to 1990s, but manipulations continued. There is quite a dissatisfaction with the privileges and subsidies that different countries grant to big industries. The latest manipulation example is the unclear status of three countries' publicly funded carbon capture investments in oil and environmental technologies. The situation is complex. The oil industry keeps the industrial secret on processes and chemical formulations, exacerbating the perception of hydrofracture. The public expresses a rejection of the unknown about hydrofracture additives. In turn, the industry resents the accusations and qualifiers that the public gives to professionals in the oil industry. The conflict reveals a failure to apply ESG (Environment, Social and Corporate Governance) principles in corporations, the underdevelopment of Corporate Social Responsibility in several of the industries and indirectly of investors ("stockholders"). There are two critical plans at the project level: the Social Management Plan, Induced Migration, Protection of the Economy and Local Work, and the Communications Plan to the Population and Local Governments (including emergencies). The titles vary widely from country to country, but the contents are similar. Both plans are approved by the authorities and applied by the engineers who designed the project to obtain the Environmental License and the most necessary license even if it is not regulated, which is the "social license" of the neighbours to operate. In the event of any environmental nuisance, neighbours can request both plans in addition to the company's Annual Sustainability Reports. Any inaccuracy and greenwashing must be clarified with the corporation, discussed with the authorities or in extreme cases, which I do not suggest using, airing it in the media clearly and presenting it to the authorities.

(b) Exclusion of local inhabitants. This case only arises when hiring policies are inadequate to the local reality, and the industry perceives local labour as poor quality or low "work ethic." This exclusion responds to a failure of the Social Impact Assessment study and the weakness of Corporate Social Responsibility, and in some cases, the manipulation of the local political environment. In general, the Social Management Plan, induced migration, protection of the economy and local work includes the training or education of local personnel to perform from manual and service tasks, to retrain or re-educate the local population on new skills required by the activity. The interested professional must request the Social Management Plan, induced migration, protection of the economy and local work to understand and face these cases.

c) Local inflation with an impact on the resident population. Local inflation is an unwanted aspect, but it is a natural result of increased local economic activity. The increase in circulating money held by project workers can put local people not linked to the project at a disadvantage. This case is one of the points of the Social Impact Study. This study must have originated the Social Management Plan, induced migration, protection of the economy and local work that includes this aspect. In many cases, opposition to hydrofracture comes from the fear of local inhabitants being marginalized by the change and the economic capacity of the neighbours who did achieve a position in the company. There are no unique or easy solutions at this point. The engineering firm in charge of studies and designs must conduct an excellent socioeconomic study of this aspect and propose appropriate solutions.

 

5- Global effects

 

a)     Increase in CO2 from natural gas & oil use impacting climate change. This is a real impact and one of the least addressed in hydrofracturing projects. The final consequence of exploiting fossil hydrocarbons from hydrofracturing is more carbon to be released into the atmosphere. The natural solution is to articulate the volume of CO2 to be released within CO2 capture projects. This articulation implies entering fully into the mechanisms of carbon bonds and in the final coordination with the specific tools for capturing and retaining CO2. This part of the studies and designs is not yet regulated, but the logical part indicates that the best way to achieve carbon capture is that at the time the product is sold, the carbon credits acquired are transferred to it. To link products sold and bonds requires that the resource extractor is the one who obtains the carbon bonds. The market principles require that the seller and buyer report the CO2 equivalent involved and the bonds traded in each transaction to the government. Note that part of the released carbon comes from the process and the machinery; this is a CO2 that the producer must report and assume. It is still not customary to request the Climate Effects Mitigation and Compensation Plan with a zero balance. Still, it is one of the most critical plans overdue for regulation. This Plan must be adjusted to the country's policies on climate change and be coordinated with the Plan for compliance with international ESG policies (Environmental, Social and Corporate Governance). This Plan is also unregulated in most countries.

 

Remember that it is the task of the interested persons to identify the critical points and request the measures considered in the specific management plan of the project. It is essential to insist that one particular point be assessed for each impact the community thinks of interest and included in the appropriate management plan.

If these reports and plans do not exist in many countries, the person concerned, with just cause, can ask the environmental authority to request their preparation. Also, in most countries, before construction starts, any person can request the writing of specific reports and Management Plans.

However, the most complex situation is the emission of CO2 from the use of carbon-rich fossil fuels. The best strategy to achieve a zero balance is to make the oil industry acquires the carbon bonds and the product sold along with the proportion of the carbon credits. In this way, the responsibility is not evaded by third parties, the object is fulfilled, and at each step of the fuel supply chain, zero balance is obtained.

Attending to the points above serves to give a somewhat more rational basis to the hydrofracture process and agree on the conditions of when not and when yes.

Here is an explanation that is exceptionally complex and requires tact and outstanding professionals in the social and communications area in the project supporting environmental professionals:

·  For project owners, business investors, design engineers, and science professionals, fracking opponents are highly emotional and unreasonable.

·  For opponents of fracking, project owners, corporate investors, design engineers, and science professionals are highly emotional and unreasonable.

Both groups accuse each other of the same thing, both are right, and at the same time, both are wrong. And as in all human relationships, the more they scream, the more polarized each becomes. Nothing convinces you more than repeating your arguments out loud.

Owners and investors, and their STEM professionals usually view the issue from the perspective of finance and economic capital from the development of the resource. They assure that the activity will generate economic growth and improve the quality of life. But, they do not have the concept of the planet as a single, closed system with limited resources. In terms of their economic vision, social and environmental issues are externalities. Things external to the project should not be considered since they are a burden, such as was previously regarded collateral damage in military operations. Stuff outside the project should be ignored or taken for granted in private capital rights, finance, laws and the market economy (Spoiler: this is not true for markets). Owners and investors often complain about regulatory instability when governments, via regulation, include externalities within project costs.

I have found that people in this group are highly emotional in individual rights, private property, and the so-called "reality" of hard money (money talks!) And in their position, they are much more absolutist than the people opposed to fracking with their green idealism. And if they are not agitating in the street, it is because they have the economic power and are lobbying the institutions of the state.

Opponents of fracking usually view the issue from the perspective of natural capital, the quality of the environment, experiential capital, and the future of culture and life on the planet. The meaning they have about developing the fossil mineral resource is that exploiting it will affect the quality of life. Unfortunately, they lack the vision of the development of economic capital to improve the environment and quality of life. They have the correct concept of the planet as a single, closed-system unit with limited resources. In terms of a green and real economy, social and environmental issues belong to the effects and impacts of the project that must be avoided, reduced, mitigated and compensated, where the concept of externality is false. In this greener vision, laws and regulations are made so that investors and companies follow the "Kaldor-Hicks Improvement" principle over the "Pareto Principle." Both current and future individuals can enjoy a healthy environment and the same opportunities and resources that we have today.

People in this group tend to find themselves exasperated by their inability to express their opposition clear, and often in their exasperation, they confuse their own arguments. They go out to agitate in the streets and to disseminate by electronic means various notions without basis and to support ideas somewhat unhinged in their sense of urgency and the suffocation of feeling that they are not heard. And in the barrage of confusing ideas and memes avalanches, politicians are intimidated and give in to measures that hurt the interests of everyone, including both investors and opponents of fracking, but politicians keep votes.

In general, opponents show in the writings that they are as emotional with their radical ideas about fracking as investors and project owners with their emotional ideas about the economy, private capital and the reality of hard money.

Interestingly, when people from both groups set out to read and understand the other side, the possibility of rational agreements is very high, and the points for reaching agreements multiply. This expansion of agreement possibilities is especially true when they realize that those in the other group are coherent and relatively rational, with different points of view.

One of the most complex points is when both sides consider the other group inconsistent with principles or actions. Incoherence is one of the biggest obstacles in this type of confrontation. Any inconsistency is perceived as falsehood, evil intent or the pursuit of harm. And any perceived falsehood or evil intention blocks the possibility of agreement.

Consequently, the company that owns the project must prepare for each hydrofracture project 37 documents, mostly management plans and at least two insurance policies. All documents and Plans must be coherent and coordinated, have their own resources and be assigned to clear positions in its organizational chart. In bold are highlighted the most important studies and plans for the subject required by the general public. These are:

 

1.     Environmental impact assessment

2.     Health Impact Assessment

3.     Social impact assessment

4.     Geophysical risk assessment

5.     Environmental Risk Assessment or Study

6.     Infrastructure adaptation plan in the project area

7.     Communications plan to the population and local governments (including emergencies)

8.     Erosion control and soil protection plan

9.     Compliance plan with international ESG policies

10. Hydro-fracture water management plan and aquifer protection

11. Rainwater and Storm Management Plan

12. Management plan for natural areas and areas in recovery

13. Waste and hydrofracture waste management plan for construction and operation

14. Management plan for invasive and undesirable animal species

15. Management plan for vulnerable (or endangered) animal and plant species

16. Management plan for invasive plant species, weeds and plant pathogens

17. Management plan for poisonous, toxic, aggressive and dangerous species

18. Drilling water and sludge management plan

19. Management plan for vectors and parasites important for human and animal health

20. Natural gas management plan, gas incineration and burning in torches and teas

21. Health Impact Management Plan

22. Heavy Traffic Management Plan

23. Social management plan, induced migration, protection of the economy and local work

24. Climate change mitigation plan (zero balance in-process and final product)

25. Water Monitoring Plan

26. Air quality monitoring plan

27. Noise and vibration monitoring plan

28. Monitoring and control plan for leaks of natural gas and other gases

29. Risk reduction and prevention

30. Prevention and management plan for induced seismicity for the area of influence

31. Biodiversity protection and management plan,

32. Land claim and end-use Plan

33. Seismicity management plan

34. Emergency Response plan (including leaks, spills, fires, etc.)

35. Final decommissioning and reclamation plan (with expected lands' end-use)

36. Land use plans of local municipalities and coordination of expected end-use

37. Claim plan compliance policy or Insurance

38. Policies and Insurance of coverage of the reduction and emergency response plan

39. Annual Reports of Sustainability and Greenhouse Gases, atmospheric and surface and deep water discharges, ISO 14001 Environmental Management System report, compliance with the Environment, Society and ESG Corporate Governance policies, and others mandated by law

 

For their part, opponents of the fracking project can request the above documents that address more than 95% of their concerns; but they must be clear and concrete in their questions. And they must be precise in the requirements of when mitigation or compensation of an effect or impact is acceptable and when it is not. Please remember that absolutes do not allow negotiation.

Based on existing laws, government entities must be clear in mediation to achieve the risk and final compensation acceptable to society.

Politicians must project their plans and vision of the future in modifying the laws that allow an acceptable risk and compensation following the rules of the democratic game.

Environmental journalists and information leaders should understand and explain the conditions that make risks and trade-offs acceptable to present and future inhabitants. And in doing so, they must clearly state the origin or source of the observation or idea and the reasons that assist both. Being impartial on environmental issues is not an absolute necessity, as long as the journalist or person expresses their preferences and reasons clearly and presents the ideas and arguments with loyalty to the original author's idea.

The above sounds good, but to apply it, we must always bear in mind that the "Right to Know or Know" by Rachel Carson (1962) always implies the "Clifford Principle of Epistemic Responsibility" (1877) and believe only in what we have sufficient evidence.

The ancient Greeks and the old Castilians rightly said that "beauty is in the harmony of the whole present in the details."

But also, the Anglo-Saxons say with sarcasm that "The devil is in the details" said that alludes to the trap or the deceptive hidden in the details. Something that may seem simple will surely be full of complicated details that will cause problems.

For these cases is that there are environmental professionals.

Commented literature

1- See: Nationa Geographic Society, How Hydraulic Fracturing Works: https://www.nationalgeographic.org/media/how-hydraulic-fracturing-works/

2- Clifford's Principle of Epistemic Responsibility (1877) in Chignell, Andrew, "The Ethics of Belief," The Stanford Encyclopedia of Philosophy (Spring 2018 Edition), Edward N. Zalta (ed.), URL = https://plato.stanford.edu/archives/spr2018/entries/ethics-belief/

3- Carson, Rachel (1962). Silent Spring. Houghton Mifflin. pp. 13, 278 pp.).

 

 

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