Patent Publication Number: US-2023152288-A1

Title: Apparatus and methods for reducing fugitive gas emissions at oil facilities

Description:
CROSS REFERENCE TO RELATED APPLICATION 
     The present application is a continuation of U.S. patent application Ser. No. 17/849,531 entitled “APPARATUS AND METHODS FOR REDUCING FUGITIVE GAS EMISSIONS AT OIL FACILITIES,” and filed 24 Jun. 2022 by DAVID L. ARMITAGE, which is a continuation and claims priority to U.S. patent application Ser. No. 17/550,918 (now U.S. Pat. No. 11,408,870) entitled “APPARATUS AND METHODS FOR REDUCING FUGITIVE GAS EMISSIONS AT OIL FACILITIES,” and filed 14 Dec. 2021 by DAVID L. ARMITAGE; which is a continuation of U.S. patent application Ser. No. 16/946,587 (now U.S. Pat. No. 11,215,593) entitled “APPARATUS AND METHODS FOR REDUCING FUGITIVE GAS EMISSIONS AT OIL FACILITIES,” filed 29 Jun. 2020 by DAVID L. ARMITAGE; which is a continuation of U.S. patent application Ser. No. 16/517,586 (now U.S. Pat. No. 10,697,947) entitled “APPARATUS AND METHODS FOR REDUCING FUGITIVE GAS EMISSIONS AT OIL FACILITIES,” and filed 20 Jul. 2019 by DAVID L. ARMITAGE; which claims priority to U.S. Provisional Patent Application No. 62/851,563 entitled “APPARATUS AND METHODS FOR DETECTING AND REPORTING ENVIRONMENTAL CONDITIONS,” and filed 22 May 2019 by DAVID L. ARMITAGE and U.S. Provisional Patent Application No. 62/795,608 entitled “APPARATUS AND METHODS FOR DETECTING AND REPORTING ENVIRONMENTAL CONDITIONS,” filed 23 Jan. 2019 by DAVID L. ARMITAGE. The entirety of the aforementioned applications are incorporated herein by reference for all purposes. 
    
    
     TECHNICAL FIELD 
     This disclosure pertains generally, but not by way of limitation, to systems and methods for reducing fugitive emissions. In particular, the system and methods described herein provide remote monitoring of oil facilities that are prone to leaking natural gas. 
     BACKGROUND 
     Monitoring and reducing air pollution is critical to our ecosystem. Historically, air monitoring has been an imperfect science including visual diagnostics or other human senses (e.g. hearing, smelling, etc.). Recently, portable and handheld sensors have been utilized to sample air as part of simple air monitoring. These handheld sensors have been utilized to locate emission sources (e.g. methane emission—a chemical compound that is the main constituent of natural gas). Methane is an attractive fuel, however capturing and storing it becomes difficult. Evidence of this difficulty is that atmospheric methane concentration has increased by about 150% since 1750 which is a problem because methane increases total radiative forcing from greenhouse gases (i.e. causing global warming). While monitoring and reducing air pollution is critical, the above human and/or sensor systems have had limitations (e.g. being non-simultaneous, inaccurate, overly-complex, expensive, etc.). 
     SUMMARY 
     The detection and reporting of pollution from an oil facility is important for a variety of reasons (e.g. corporate performance, quality of environment, regulatory requirements, etc.). For example, an oil facility removing natural gas (and/or oil) from an underground reservoir utilizes equipment (e.g. pumpjacks, holding tanks, valves, pipes, etc.) that requires maintenance. Occasionally, this equipment releases pollution into the atmosphere. This release into the atmosphere is called ‘fugitive gas emission’ or generically ‘pollution’ that should be detected and reported so corrective action may be taken. 
     To address emission/pollution, the disclosed system monitors, detects, and reports the differential concentrations of gas from a population of monitors located around the perimeter of a site. Differential concentrations of gas from a population (of monitors located in a monitored area) indicates presence of a leak. An oil facility configured with the present system can sense the increase/presence of emissions by comparing readings from a plurality of pollution monitors. Each pollution monitor utilizes a logic control system to read at least one pollution sensor; furthermore, the aggregation of pollution monitors presents the sensed site data to determine if there is a leak. The pollution leak can be addressed accordingly (e.g. noted, repaired, observed, etc.). 
     One general aspect of a pollution monitor for an oil facility may include a housing having an interior and an exterior provided with a first venturi opening formed in the housing to allow airflow between the exterior and interior. The housing may further include a second venturi opening configured to allow airflow between the interior and exterior with an airstream path in the interior between the first venturi opening and the second venturi opening. The pollution monitor further includes an electronics package positioned in the interior of the housing adjacent to the airstream path. The electronics package may include a pollution sensor electrically interfaced with the electronics package and configured to output a signal representative of an airborne pollutant concentration. The electronics package may further include a communications module electrically interfaced with the electronics package and configured to transmit the airborne pollutant concentration. The pollution monitor may further include a panel mount attached to the housing including a top and a pitch angle formed between the top and a global-horizontal plane. The pitch angle may be greater than zero degrees and have a solar panel attached to the top of the panel mount. The solar panel is electrically interfaced with the electronics package and configured to drain water. The solar panel may be configured to maximize solar charging and have a power conductor electrically interfaced with the solar panel. The power conductor terminates at the electronics package and may pass through the housing. All of these cooperate to provide a system for reducing fugitive gas emissions at an oil facility as described herein. 
     In another general aspect, a method for sampling air pollution at an oil facility may include a pollution monitor having a housing. The housing may be configured to receive one or more components and to protect the components from outdoor environmental conditions. These optional components may include an electronics package disposed in the housing, and a pollution sensor in electrical communication with the electronics package. The pollution sensor may be configured to output a signal representative of a pollutant concentration. The pollution monitor may further include a location defined by geolocation and a physical sampling system in electrical communication with the electronics package. The method for sampling may further include establishing a rule for invoking a sampling event, and monitoring for breach of the rule. Upon breach of the rule, the pollution monitor may be invoked to initiate sampling of air pollution by capturing a sample of air with the physical sampling system, and storing the location of the sample of air. 
     In another general aspect, a method for reporting atmospheric pollution originating at an oil facility may include providing a first pollution monitor having a housing configured to receive components of the pollution monitor and to protect the components from environmental conditions. The components may include an electronics package adjacent to the housing. Furthermore, the components may include a first pollution sensor in electrical communication with the electronics package, and the first pollution sensor may be configured to report atmospheric level of a first amount of pollution. The first pollution monitor may include a first location defined by a geographic coordinate. The method may include providing a second pollution monitor including a housing configured to receive components of the second pollution monitor and to protect the components from environmental conditions. The second pollution monitor may include an electronics package adjacent to the housing and a second pollution sensor in electrical communication with the electronics package. The second pollution sensor may be configured to report a second amount of pollution. The second pollution monitor may include a second location defined by a geographic coordinate that is different than the first location. The method may further include comparing the first amount of pollution reported by the first pollution sensor to the second amount of pollution reported by the second pollution sensor. The method may further include reporting atmospheric pollution originating at the oil facility when the first amount of pollution is different than the second amount of pollution. And, the method may create, after the reporting, instructions to address the pollution originating at the oil facility. 
    
    
     
       BRIEF DESCRIPTION OF THE DRAWINGS 
       The accompanying figures of the drawing, which are included to provide a further understanding of general aspects of the system/method, are incorporated in and constitute a part of this specification. These illustrative aspects of the system/method, and together with the detailed description, explain the principles of the system. No attempt is made to show structural details in more detail than is necessary for a fundamental understanding of the system and various ways in which it is practiced. The following figures of the drawing include: 
         FIG.  1    is a perspective view a monitored area (e.g. an oil facility configured as a wellsite) provided with a plurality of pollution monitors, according to an illustrative embodiment of the present disclosure; 
         FIG.  2    is a perspective view of an illustrative pollution monitor attached to a vertical object (e.g. a T-post), according to an illustrative embodiment of the present disclosure; 
         FIG.  3    is a perspective view of an illustrative pollution monitor in an exploded condition, according to an illustrative embodiment of the present disclosure; 
         FIG.  4    is a perspective view of the pollution monitor of  FIG.  3    in an assembled condition; 
         FIG.  5    is a side elevation view of an illustrative pollution monitor wherein an insulating body is configured as a bird habitat, according to an illustrative embodiment of the present disclosure; 
         FIG.  6    is a cross-section side elevation view of the pollution monitor of  FIG.  4    taken across plane  6 - 6 ; 
         FIG.  7    is a perspective view of an electronics package of an illustrative pollution monitor wherein a top is remove for illustrative purposes, according to an illustrative embodiment of the present disclosure; 
         FIG.  8    is a perspective view of the electronics package of  FIG.  7    in an exploded condition; 
         FIG.  9    is a side elevation view of the electronics package of  FIG.  7    in an exploded condition; 
         FIG.  10    is a perspective view of the electronics package of  FIG.  7    in an assembled condition including a top; 
         FIG.  11    is a bottom plan view of the electronics package of  FIG.  10   ; 
         FIG.  12    is a top plan view of the electronics package of  FIG.  10   ; 
         FIG.  13    is a side elevation view of the electronics package of  FIG.  10   ; 
         FIG.  14    is a side elevation view of the electronics package of  FIG.  10   ; 
         FIG.  15    is a functional schematic of illustrating components of a pollution monitor, according to an illustrative embodiment of the present disclosure; 
         FIG.  16    is a perspective view of illustrative components of an electronics package of the pollution monitor, according to an illustrative embodiment of the present disclosure; 
         FIG.  17    is a side elevation view of the electronics package of  FIG.  16   ; 
         FIG.  18    is a top plan view of the electronics package of  FIG.  16   ; 
         FIG.  19    is a bottom plan view of the electronics package of  FIG.  16   ; 
         FIG.  20    is a schematic diagram of illustrative components of a pollution monitor noting additional figures with enlarged details, according to an illustrative embodiment of the present disclosure; 
         FIG.  21    illustrates input connectors of the schematic diagram of  FIG.  20    including a USB connection, a solar connection, an analog switch, a battery holder, and a battery connector; 
         FIG.  22    illustrates meteorological sensors of the schematic diagram of  FIG.  20    including a temperature and humidity sensor and a microphone; 
         FIG.  23    illustrates pollution sensors of the schematic diagram of  FIG.  20    including a methane sensor and an external environmental sensor; 
         FIG.  24    illustrates miscellaneous components/features of the schematic diagram of  FIG.  20    including mounting holes, fiducials, and a connector; 
         FIG.  25    illustrates a location sensor of the schematic diagram of  FIG.  20    including a global positioning sensor (GPS); 
         FIG.  26    illustrates a communications platform of the schematic diagram of  FIG.  20    including a cellular protocol system, an antenna, and a status indicator; 
         FIG.  27    illustrates expansion connectors of the schematic diagram of  FIG.  20    including an analog expansion connector, a digital expansion connector, and a power expansion connector; 
         FIG.  28    illustrates miscellaneous components/features of the schematic diagram of  FIG.  20    including an external particulate sensor and a boost converter; 
         FIG.  29    illustrates power components of the schematic diagram of  FIG.  20    including a power distribution switch; 
         FIG.  30    illustrates miscellaneous components of the schematic diagram of  FIG.  20    including a voltage-level translator, a pollution sensor (e.g. volatile organic compound sensor), and a voltage regulator; 
         FIG.  31    illustrates a sensor of the schematic diagram of  FIG.  20    including a pollution sensor; 
         FIG.  32    is a top plan view of an oil facility (e.g. a wellsite) having an emissions source (also referred to as a leak, a leak event, etc.), the oil facility is monitored by an illustrative configuration of a plurality of pollution monitors, according to an illustrative embodiment of the present disclosure; 
         FIG.  33    illustrates a graph of outputs from the plurality of pollution monitors of  FIG.  32   ; 
         FIG.  34    is a top plan view of a rural oil facility and an illustration of a vehicle carrying a technician and a mobile device to/from the rural oil facility, according to an illustrative embodiment of the present disclosure; 
         FIG.  35    is a top plan view of an oil facility with an illustrative pollution monitor system illustrating sound transfer from a leak to pollution monitors, according to an illustrative embodiment of the present disclosure; 
         FIG.  36    is a top plan view of an oil facility configured with a pollution monitoring system, according to an illustrative embodiment of the present disclosure; 
         FIG.  37    is a perspective view of an illustrative pollution monitor configured with an optional physical sampling system (e.g. an air sampling system configures as a summa canister), according to an illustrative embodiment of the present disclosure; 
         FIG.  38    is an information display, in data modality, configured as a website page served on the internet, according to an illustrative embodiment of the present disclosure; 
         FIG.  39    is an information display, in map modality, configured as a website page served on the internet, according to an illustrative embodiment of the present disclosure; 
         FIG.  40    is a perspective view of an illustrative pollution monitor configured with an optional meteorological system (e.g. a wind sensor), an optional air conveyance tube, an optional bird deterrent mechanism, and optional booster solar panels, according to illustrative embodiments of the present disclosure; 
         FIG.  41    is a perspective view of an illustrative pollution monitor configured with a vertical object, according to an illustrative embodiment of the present disclosure; 
         FIG.  42    is a front elevation view of the pollution monitor of  FIG.  41   ; 
         FIG.  43    is a left side elevation view of the pollution monitor of  FIG.  41   ; 
         FIG.  44    is a back elevation view of the pollution monitor of  FIG.  41   ; 
         FIG.  45    is a right side elevation view of the pollution monitor of  FIG.  41   ; 
         FIG.  46    is a top plan view of the pollution monitor of  FIG.  41   ; 
         FIG.  47    is a bottom plan view of the pollution monitor of  FIG.  41   ; 
         FIG.  48    is a perspective view of a pollution monitor, according to an illustrative embodiment of the present disclosure; 
         FIG.  49    is a front elevation view of the pollution monitor of  FIG.  48   ; 
         FIG.  50    is a left side elevation view of the pollution monitor of  FIG.  48   ; 
         FIG.  51    is a back elevation view of the pollution monitor of  FIG.  48   ; 
         FIG.  52    is a right side elevation view of the pollution monitor of  FIG.  48   ; 
         FIG.  53    is a bottom side perspective view of the pollution monitor of  FIG.  48   ; 
         FIG.  54    is another bottom side perspective view of the pollution monitor of  FIG.  48   ; 
         FIG.  55    is a bottom plan view of the pollution monitor of  FIG.  48   ; and 
         FIG.  56    is a top plan view of the pollution monitor of  FIG.  48   . 
     
    
    
     In the appended figures, similar components and/or features may have the same numerical reference label. Further, various components of the same type may be distinguished by following the reference label with a letter. If only the first numerical reference label is used in the specification, the description is applicable to any one of the similar components and/or features having the same first numerical reference label irrespective of the suffix. 
     DETAILED DESCRIPTION 
     The ensuing description provides preferred illustrative embodiments only, and is not intended to limit the scope, applicability or configuration of the disclosure. Rather, the ensuing description of the preferred illustrative embodiments will provide those skilled in the art with an enabling description for implementing a preferred illustrative embodiment. It is understood that various changes may be made in the function and arrangement of the elements without departing from the spirit and scope set forth in the appended claims. It should be noted that while the following description is configured for an oil and gas facility, other areas that may be configured with the present system. For example, the system may be utilized at locations ranging from rural marshlands to urban industrial facilities. Other examples of monitored areas include, but are not limited to: beaches (for red-tide blooms), gas stations, painting facilities, parking lots, cattle feed lots, rendering facilities, propane refilling stations, truck servicing bays, etc. As used herein, the term ‘monitored area’ means any location where pollution presence (in or around) is monitored. The monitored site may be relatively large or, in one example configured as a wellsite, relatively small of about 0.2 to 2 acres. One application for the present pollution monitor is at/in/near ‘oil facilities’ such as: well sites, drilling rigs, service rigs, offshore platforms, refineries, petrochemical plants, gas plants, pipelines, tank farms, wellheads, pump jacks, etc. 
     With reference to  FIG.  1    showing a monitored area  90  at an oil facility  100 , the system for reducing fugitive gas emissions may detect and report pollution at the oil facility  100  with pollution monitors  102 ,  104 ,  106  and  108 . In general terms, the monitored area  90  may be located in an oil-producing region and oil facility  100  may include various industrial items such as pumpjacks  92 ,  94  and holding tanks  96 ,  98 . The pumpjacks and holding tanks are in fluid communication with each other by a network of pipes (not shown). Oil and/or gas is pulled from an underground reservoir (not shown) via the pumpjack  92  and distributed to the holding tank  96 . Occasionally, constituents of oil/gas (e.g. hydrocarbons such as: methane, ethane, butane, pentane, hexanes, etc., and other fluids in either liquid or gas state, e.g.: nitrogen, carbon dioxide, oxygen, hydrogen, rare gasses, etc.) are discharged into the atmosphere. This discharge into the atmosphere is called fugitive emission and/or pollution that is man-made (anthropogenic). For example, if a packing gland of the pumpjack  92  is expired, hydrocarbons may be discharged (i.e. leak) from the packing gland. The oil facility  100  configured with the present system can sense the increase/presence of emissions by comparing readings from one or more of the pollution monitors  102 ,  104 ,  106 ,  108  as described herein. 
     With reference to  FIG.  2    showing an illustrative pollution monitor, the pollution monitor  108  may be configured in any variety of forms such as the useful configuration disguised as a birdhouse. The term ‘birdhouse’ is synonymous with ‘bird habitat’ and refers to any artificial interior portion capable of receiving and sheltering at least one bird from the elements. Passage from the interior portion to the exterior portion is enabled by a bird passage as described herein. In the illustrated configuration, the pollution monitor  108  may include a ‘panel mount’ configured as an insulating body  110  having a top  112  and an oppositely disposed bottom  114  separated by a box  116 . The box  116  includes perimeter walls referred herein as a front face  118 , a left side  120 , a back face  122 , and a right side  124 . The box  116  is a structure that has an interior area  126  ( FIG.  5   ) that is substantially blocked from ambient conditions of an exterior area. In one embodiment, the front face  118 , left side  120 , back face  122 , right side  124 , top  112 , and bottom  114  are made of wood. However, the insulating body  110  can be made in a large variety of configurations with a variety of materials. As used herein the term ‘panel mount’ means a structure capable of supporting a solar panel (e.g. the insulating body  110 , a fixed bracket, one or more angle brackets, a pivot, etc.). 
     With continued reference to  FIG.  2   , the insulating body  110  is capable of shielding heat at the insulating body top  112  from transferring to the insulating body bottom  114  (i.e. blocking heat from transferring through the insulating body  110 ). As used herein, the term ‘insulating body’ means a structure designed to block heat transfer from a top surface to a bottom surface. To be clear, while most materials provide some level of insulation, the present configuration of the panel mount includes an insulating body that intentionally blocks heat transfer. While a variety of structures/materials may be deployed to block heat transfer, specific examples include: foamed plastic sheet, spun fibers compressed into a board, natural organic(s) formed into a planar object, wood board, a birdhouse, concrete structure, a ribbed plastic structure with airgaps, etc. While the insulating body  110  may be a variety of thicknesses, one configuration includes a thickness of eight to ten inches. In another configuration, the insulating body  110  may be about an inch thick, or 0.25 inches to two inches, or the thickness may be between two and eight inches depending on the particular configuration. In one specific configuration, the insulating body includes a large interior portion of stagnant air configured to receive a bird which is eight inches at the front face  118  and ten inches at the back face  122 . 
     With continued reference to  FIG.  2   , the pollution monitor  108  may be attached to any of a variety of ‘vertical objects’, such as the T-post  130  as illustrated. The T-post  130  is a readily installable and a suitably stationary object to which the pollution monitor  108  may be attached. The T-post  130  may be configured a length of metal (e.g. steel) having a spade end  132  and an oppositely disposed top end  134  as illustrated. The T-post  130  may be configured with a spade  133  located at the spade end  132  and further configured with an anvil  135  located at the top end  134 . The T-post spade end  132  is anchored (by manual or machine impact) into ground at the monitored area  90  such that the T-post top end  134  is about, for example, 5 feet in the air. This orientation allows the top end  134  of the T-post  130  to be clear from objects such as grass, bushes, trees, buildings, snow, standing water, small animals, etc. Therefore, any reasonably elongated member of the T-post  130  (e.g. over 2 feet) may be enough to keep the pollution monitor  108  above other objects where the intended functionality can be performed. The T-post  130  (sometimes referred to herein as a ‘vertical object’) may be made of a material with a geometry that can support the pollution monitor  108 . The cross-sectional view of the T-post may, in one example, be a ‘T’ that is easily driven into the ground with a manual or pneumatic post pounder. The T-post  130  may be provided with studs ( FIG.  10   ) that prevent attached components (e.g. the pollution monitor  108  and the spade  133 ) from sliding down the T-post  130 . 
     With continued reference to  FIG.  2   , the pollution monitor  108  may be attached to the top end  134  of the T-post  130  by any of any one of a variety of mechanical means such as a U-bolt  138  ( FIG.  3   ), alternatives include, but are not limited to: band clamps, wire ties, bolts, rivets, screws, adhesive, etc. Additionally, the process of installing other pollution monitors (e.g.  104 ,  106 ,  108  shown in  FIG.  1   ) may be the same as installing pollution monitor  108  in the monitored area  90 . If powered by a solar panel (described herein), the front face  118  may generally face south when installed in North America. 
     With reference to  FIG.  3    illustrating a perspective view of the pollution monitor  108  in an exploded condition without the vertical object (T-post  130 ), the pollution monitor  108  is provided with a power system (e.g. a permanent battery, a rechargeable battery, a thermo-electric system, a hydro-electric system, etc.) such as a solar panel  140 . The solar panel  140  is a generally planar object capable of converting energy from the sun into electrons through a photovoltaic process. The solar panel  140  includes a top surface  142 , an opposite bottom surface  144 , and a power lead  146 . The solar panel top surface  142  may include silicon wafers generating electrons that flow to the bottom surface  144  and continue to an electronics package  150  via the power lead  146 . The solar panel bottom surface  144  may be attached to the panel mount (e.g. configured as the insulating body top  112 ) by any of a variety of attachment methods, such as with a pivot bracket (not shown), mechanical fasteners (not shown), or adhesive as illustrated ( FIG.  4   ). The solar panel  140  may be constructed of traditional or specialized components. Traditional methods of construction include epoxy encapsulation while more specialized construction includes ethel vinyl acetate (EVA) encapsulation with an ETFE sheet protection at the outermost surface. In one example, the solar panel  140  is configured with a number of individual solar cells that are configured to match the solar panel&#39;s maximum power point to the average charge voltage of the battery. The solar panel  140  may be separated from the insulating body  110 , or it may be provided as a number of individual panels such as individual panels attached to the front face  118 , the left side  120 , and/or the right side  124  ( FIG.  40   ). 
     With continued reference to  FIG.  3   , the electronics package  150  may include a housing  160 . The electronics package housing  160  may be made of any structural material (such as metal, wood, or plastic) and generally defines a top  162  and an oppositely disposed bottom  164 . The housing top  162  and bottom  164  are separated by a perimeter of walls, specifically a front wall  166 , a left wall  168 , a back wall  170 , and a right wall  172 . The electronic assembly  150  may be attached to the bottom  114  of the insulating body  110  via any of a variety of methods such as mechanical fasteners (e.g. screws as shown) thereby creating an internal portion  174  ( FIG.  6   ) and an exterior portion  176  (the exterior portion  176  is at ambient condition). 
     With reference to  FIG.  4    illustrating a perspective view of the pollution monitor  108  with the solar panel  140  and electronics package  150  attached thereto, the pollution monitor may be configured as a bird habitat where the insulating body  110  includes a bird passage  128  formed in the insulating body front face  118 . The bird passage  128  provides a pathway for a bird  136  ( FIG.  5   ) to move from ambient conditions at the exterior portion  176  into the interior area  126  as illustrated in  FIG.  5   . In this illustrative configuration, the pollution monitor  108  is configured as a birdhouse so that it blends, aesthetically, into the surroundings and to be a resource to benefit the environment. This illustrated birdhouse configuration (where in the insulating body  110  is shaped as a traditional birdhouse and configured to receive the bird  136 ), is useful for blocking the high heat (temperature) at the top  112  from the electronics package  150 . The insulating body  110  may take other forms ranging from a simple piece of insulating material (e.g. a low-conduction material, a plate of structural foam, a hollow box, etc.) to a more elaborate configuration as can be appreciated by one skilled in the art with the benefits and teachings of the present document. In one example, the insulating body  110  and the housing  160  may be combined in a simple enclosure such as a ‘project box’ used for housing electronics. In this project box configuration, the solar panel  140  is simply attached to one face of the box or may be held by a panel mount (either fixed or adjustable). 
     With reference to  FIG.  5    showing a side elevation view of the pollution monitor  108 , (wherein a portion of the insulating body left side  120  has been removed) the bird  136  may take shelter in the interior area  126 . Some species of birds have at least a partially insectivorous diet and insects are a source of protein for nestlings. Examples of insectivorous birds include bluebirds, dippers, flycatchers, swallows, and wrens. It may be useful to include a birdhouse with the pollution monitor  108  to avoid insects from seeking refuge in the pollution monitor  108  (either in the insulating body  110  or the housing  160  of the electronics package  150 ). 
     With continued reference to  FIG.  5   , the pollution monitor  108  may be configured such that the top  112  is able to shed rain (i.e. drain water) and positioned for maximum solar-charging, and therefore angled relative to a global-horizontal plane  10 . This global-horizontal plane  10  is useful while describing features of the environmental monitoring  108 . As used herein, the term ‘global-horizontal plane’ is a plane with a point that is colinear to local gravity direction and intersects perpendicular to the global-horizontal plane  10  (also referred to as ‘level’ as defined by a carpentry level). Therefore, the top  112  of the insulating body  110  resides in a plane that intersects the global-horizontal plane  10  at an angle of intersection referred to herein as a pitch angle  12 . The pitch angle  12  may be any non-zero angle, such as 45 degrees which is ideal for optimally positioning the solar panel  140  relative to the sun facing south in North American installations. The pitch angle  12  for North America is 35 degrees plus or minus 20 degrees, that results in the top  112  positioned normal to the sun at solar-noon on winter solstice (11:58 am on 21 Dec. 2019 in Denver, Colo.). The power lead  146  serves as part of a power conductor to move power from the solar panel  140  to the electronics package  150  via the solar connection  252  (described herein). Therefore, the power conductor configured as power lead  146  and solar connection  252  pass ‘through’ the housing  160  to deliver power from the solar panel  140  to the battery. 
     With reference to  FIG.  6    illustrating a side view of the pollution monitor  108  taken across plane  6 - 6  ( FIG.  4   ), the electronics package housing  160  may include features causing ambient air to flow into (and subsequently out of) the internal portion  174 . A simple but energy-consuming configuration is an air pump, but other configurations have proven useful. If provided with features for causing airflow, the housing  160  may include several venturi openings such as a first venturi opening  180  and a second venturi opening  182 . While any number of venturi openings may be provided in any surface of the package housing  160 , the first venturi opening  180  may be formed in the housing front wall  166  near the top  162  ( FIG.  3   ). In a similar manner, the second venturi opening  182  may be formed in the housing back wall  170  near the top  162 . When the electronics package  150  is attached to the insulating body  110 , the first venturi opening  180  and second venturi opening  182  form openings through which moving air can travel along an airstream path  183  (located in the internal portion  174  as illustrated). Moving air causes a pressure drop inside the electronics package  150  which is utilized to move air into and mixed inside the electronics package internal portion  174 . In one illustrative embodiment, the electronics package  150  may further include a sensor opening  184  formed in the bottom  164  of the housing  160 . As air moves from the first venturi opening  180  through the internal portion  174 , it moves ambient air across at least one sensor for a purpose described herein. The air ultimately escapes the housing  160  through the second venturi opening  182  (or other openings). 
     With continued reference to  FIG.  6   , the venturi openings  180 ,  182  cooperate to move air and draw ambient air across a pollution sensor  202 . The dark flow lines in  FIG.  6    illustrate the flow of air through the electronics package  150 . In addition to the pollution sensor  202 , other sensors may be placed in the flow of air for the purposes of expansive measurements and/or providing redundancy. For example, other sensors that may be substituted, augmented, placed in multiples, include but are not limited to sensors that detect fluids (e.g. methane, ethane, propane, butane, carbon dioxide, oxygen, nitrogen, hydrogen sulfide, rare gasses, etc.). 
     With reference to  FIG.  7    illustrating a perspective view of an illustrative electronics package  150 , the electronics package  150  may be provided with a logic control system  190 , a watchdog system  192 , a power management module  194 , a power supply (e.g. the solar panel  140 ,  FIG.  3   ), a battery  198 , a meteorological module  200 , at least one pollution sensor  202 , a communications module  204 , and a global positioning sensor  206 . These various electronics interact to provide the pollution monitoring functionality at the monitored oil facility. 
     With continued reference to  FIG.  7   , at the heart of the electronics package  150  is the logic control system  190  that performs operational instructions. The watchdog system  192 , if provided, is an electronic timer used to detect and recover from malfunctions of the logic control system  190 . During normal operation, the logic control system  190  may regularly reset the watchdog timer  192  to prevent it from elapsing, or ‘timing out.’ The power management module  194  can be any of a variety of management systems to provide power to the electronics package  150 . In the embodiment illustrated, the power management module  194  manages performance and reports quality and status of the power generated by the solar panel  140  ( FIG.  4   ) and subsequently provided to the battery  198 . The meteorological module  200 , if provided, includes one or more sensors for monitoring environment (e.g. wind speed, direction, temperature, humidity, atmospheric pressure, rainfall, lighting, etc.). The meteorological module  200  may be interfaced with the logic control system  190  via connected or wireless devices (not shown) that provide serial line communication or other protocols utilized by those skilled in the art. 
     With continued reference to  FIG.  7   , the pollution sensor  202  may be interfaced with the logic control system  190  via serial line communication or other protocol. While some varieties of the pollution sensor  202  may be mounted outside the electronics package  150 , one particular type of sensor may be mounted in the internal portion  174  of the electronics package  150 . As best illustrated in  FIG.  7   , a pollution sensor  202  may be a hydrocarbon sensor capable of measuring a few parts per million (PPM) of hydrocarbons (specifically volatile organic compounds). This hydrocarbon sensor version of the pollution sensor  202  may be at a low temperature and dry location where ambient air is exposed to the pollution sensor  202 . The pollution sensor  202  may detect trace amounts of pollution. As used herein, the terms pollution and pollutant are any substance introduced into the environment with undesired effects, or adversely affects the usefulness of a resource. A pollutant causes long- or short-term damage by changing the growth rate of plant or animal species, or by interfering with human amenities, comfort, health, or property values. 
     As used herein, the term ‘pollution sensor’ refers to air pollution devices that detect and monitor the presence of air pollution in the surrounding area. There are various types of air pollution sensors such as particulate matter (PM) sensors and gas phase (GP) sensors. The sensor receives an airflow which passes over at least one electrochemical cell that responds to pollutants. To isolate one pollutant or the other, a separate measurement is needed in field tests. Gas-sensitive semiconductor gas sensors (sometimes referred to as heated metal oxide semiconductor, HMOS) are based on the property that certain metal oxides exhibit a change in electrical resistance in the presence of a target gas. This resistance change is caused by a loss or gain of surface oxygen species via reaction with the target gas. There is a well-defined relationship between gas concentration and change in electrical resistance which leads to a measurement of the target gas concentration. 
     With continued reference to  FIG.  7   , the communications module  204  may be provided for sending and/or receiving data between a communications infrastructure (e.g. wired, satellite, cellular, long range radio, shortwave radio, Wi-Fi, mesh, or other variants of communication currently utilized in industry or later introduced). The global positioning sensor  206 , if provided, may be used for obtaining and reporting location of the pollution monitor  108 . In one configuration, the global positioning sensor  206  utilizes satellites to determine its location and may report the installation location of the pollution monitor  108  within a few meters, so deployment of system at the oil facility  100  is relatively quick and the global positioning sensor  206  and logic control system  190  cooperate to send the location via the communications module  204 . 
     With reference to  FIG.  8    illustrating a perspective view of the electronics package  150  in an exploded condition, the housing  160  may be configured into two pieces retaining their original references as top  162  and bottom  164 . The bottom  164  may be configured with the first venturi opening  180  and the second venturi opening  182  formed into the front wall  166  and back wall  170 , respectively. Additional openings (e.g.  178 ,  179 ,  FIG.  7   ) may be formed into the housing  160  as illustrated. The top  162  may be configured with protrusions formed therein to extend over the openings, such as a brim  163  formed on the top  162  adjacent to the first venturi opening  180 . The brim  163  may substantially block horizontally-moving water and debris from entering the internal portion  174 . Furthermore, the brim  163  may be (essentially) parallel to the first venturi opening  180  and the front wall  166  (in which the first venturi opening  180  is formed). It is important to note that the use of the term ‘parallel’ means essentially parallel and not to a high degree of parallelism because manufacturing limitations cause draft angles. This configuration may establish an airgap that is in fluid communication with the internal portion  174  and the exterior portion  176  of the housing  160 . Similar protrusions (e.g. brims) may be formed into the top  162  as illustrated for protecting the openings (e.g.  180 ,  178 ,  179 ) from water and debris from entering the internal portion  174 . 
     As illustrated in  FIGS.  8 - 14   , the electronics package  150  may be configured to interface with the panel mount configured as the insulating body  110  ( FIG.  2   ) and electrically connected (i.e. electrically coupled, or simply plugged in) to the solar panel  140  ( FIG.  2   ). Alternatively, in one configuration, the pollution monitor may be temporarily deployed wherein the battery  198  ( FIG.  7   ) provides enough power for the temporary deployment. If the deployment is temporary, the electronics package  150  may be relatively small without a solar panel and it may be camouflaged for discrete deployment. 
     With reference to  FIG.  15    illustrating a functional schematic of various components of an illustrative pollution monitor  108 , general communications of the electronics package  150  may be performed by the communications module  204  (e.g. on separate modules such as a LAN communications module  208  and/or a WAN communications module  210 ). As described herein, the pollution sensor  202  may be verified by separate a physical sampling device(s)  211  such as an air quality sampling module  212 , a soil sampling module  214 , and/or a groundwater sampling module  216 . If required for an application, additional modules may be provided with the electronics package  150  including, for example: a status indicator  218  (also shown in  FIG.  10   ), a video recording module  220  ( FIG.  11   ), a proximity-orientation-movement module  222  ( FIG.  11   ), and/or a clock module  224 . One example of the air quality sampling module  212  is described later herein and shown in  FIG.  37   . Additionally, an example of the groundwater sampling module  216  is described later herein and shown in  FIG.  40   . The status indicator  218  may or may not be present on the pollution monitor  108 —for example, the status indicator  218  (also shown in  FIG.  10   ) may be at least one LED that lights up on the housing  160  or it may be wirelessly transferred to a remote device (e.g. a smartphone or handheld electronics device, for example). The video recording module  220 , if provided, may record in the visible spectrum or may be operating in a non-visible spectrum such as infrared. The proximity-orientation-movement module  222  may be capable of reporting movement of orientation or location indicating that events such as tampering or accidental falling—these events may be usually reported to a remote location via the communications module  204 . The clock module  224  can acquire current time and tracking time passage—the clock module  224  generally obtains its set-time via the global positioning sensor  206 , the meteorological module  200 , the communications module  204  (either LAN communications module  208  or WAN communications module  210 ) or from other remote system such as the NIST atomic clock and its network-connected services. Other examples include network provided time stamps (e.g. cellular tower), internet services (e.g. cloud server), etc. The time tracked by the clock module  224  may be periodically checked by the logic control system  190  during, for example, a wakeup routine or periodically (e.g. every 12-hours). In each of the individual pollution monitors  102 ,  104 ,  106 , and  108 , the times are synchronized in order to carefully track events. At least one of the individual components of the electronics package  150  has a unique identifier number such as, for example, the EMEI or MAC address of the communications module  204  or a serial number for the logic control system  190 . The various modules cooperate to enable various functions of the pollution monitor  108 . 
       FIGS.  16 - 19    illustrate one configuration of the electronics package  150  provided with a printed circuit board assembly  230 . The printed circuit board assembly  230  includes a circuit board  240  having a front side  242  and a back side  244 . The printed circuit board assembly  230  may further include: a USB connection  250 , a solar connection  252 , an analog switch  254 , a primary battery holder  256 , a secondary battery connector  258 , a temperature/humidity sensor  260 , a microphone  262 , a metrological connector  264 , a first pollution sensor  266  (configured as a methane sensor), a second pollution sensor  268  (configured as a primary Volitile Organic Compound, VoC, sensor), a third pollution sensor  270  (configured as a secondary VoC sensor), a physical sample connector  272 , a location module  274 , a location antenna connector  276 , a communications module  278 , a communications antenna connector  280 , a first expansion connector  282 , a second expansion connector  284 , a third expansion connector  286 , a fourth pollution sensor  288  (configured as a particulate sensor), a boost converter  290 , a power switch  292 , a voltage regulator  294 , a signal translator  296 , and other miscellaneous components required for full and optimal operation (e.g. resistors, capacitors, diodes, inductors, light emitting diodes, headers, jumpers, connectors, switches, etc.). 
     With reference to  FIG.  16    showing a perspective view of the printed circuit board assembly  230 , the front side  242  of the circuit board  240  may be populated with some of the components. In one illustrative example, the circuit board front side  242  may include the communications module  278  and the communications antenna connector  280  provided for communicating with other pollution monitors, electronic devices, communications towers, satellites, or their equivalents. The illustrative example may include the primary battery holder  256  and the secondary battery connector  258  for receiving either primary or secondary batteries for powering the pollution monitor  108 , in one example, the primary battery holder  256  receives an 18650 lithium ion secondary (rechargeable) battery  198  ( FIG.  7   ). The USB connection  250  may be provided for reprogramming or generally to interface other devices during manufacturing and/or servicing. The first expansion connector  282 , second expansion connector  284 , and third expansion connector  286  may be provided for future feature deployment. The location module  274  and location antenna connector  276  may be supplied for determining location the pollution monitor  108 . The first pollution sensor  266 , second pollution sensor  268 , third pollution sensor  270 , and fourth pollution sensor  288  are illustrative examples of a comprehensive approach to determining pollution levels in the local atmosphere of the pollution monitor as described in detail herein. The boost converter  290  may be provided to accurately supply a specific voltage to one or more of the pollution sensors in a process for improving response time and/or accuracy of readings made by the pollution sensors. The temperature/humidity sensor  260  may be provided for evaluating and reporting micro-climate of the internal portion  174  of the electronics package  150 . 
     With reference to  FIG.  17    illustrating a side elevation view of the printed circuit board assembly  230 , the back side  244  of the circuit board  240  may be populated with the solar connection  252 , the status indicator  218 , the physical sample connector  272 , and the metrological connector  264 . The front side  242  of the circuit board  240  may be configured with a daughterboard connector  298  for receiving a sensor assembly  300 . The sensor assembly  300  may include a circuit board  302  and a pollution sensor (e.g. first pollution sensor  266 ). When configured as shown in  FIG.  17   , the first pollution sensor  266  and other pollution sensors (e.g. second pollution sensor  268 , third pollution sensor  270 , fourth pollution sensor  288 ) may be configured to be in the flow of air through the housing  160  of the electronics package  150  ( FIG.  6   ) whereby the airstream path  183  ( FIG.  6   ) moves the atmospheric air across the pollution sensors. 
     With reference to  FIG.  18    illustrating a top plan view of the printed circuit board assembly  230 , the printed circuit board assembly  230  may be configured as illustrated where the communications module  278  is an assembly attached to and in electrical communication with the circuit board  240 . The printed circuit board assembly  230  may be provided with a plurality of mounting holes (e.g. mounting hole  304 ) for attaching it to the housing  160 . 
     With reference to  FIG.  19    illustrating a bottom plan view of the printed circuit board assembly  230 , the back side  244  may have the analog switch  254  configured to receive a tool (e.g. a small piece of wire, not shown) through the housing  160  for a reset procedure while in service. As best shown in  FIG.  19   , the physical sample connector  272  and the metrological connector  264  may be universal connectors (e.g. telecommunications registered jack) for interfacing with remote devices such as the sampling devices  211  or the meteorological module  200 . As best illustrated in  FIG.  10   , the physical sample connector  272 , the metrological connector  264 , and solar connection  252  extend to the outside portion of the housing  160 . 
     With reference to  FIG.  20    illustrating a schematic of one configuration of the printed circuit board assembly  230 , the details of optional and illustrative components are shown on  FIGS.  21 - 31   . While only some of these components may be utilized, others (not shown or described) may be implemented depending on the intended functionality of the pollution monitor. Therefore, the present printed circuit board assembly  230  described is illustrative and not necessarily the only configuration. 
     With reference to  FIG.  21   , the USB connection  250  may be a standard micro-USB connector commonly used in electronic devices. The solar connection  252  may be a commonly sourced barrel type connector for connecting DC power, such as the power supplied by the solar panel  140  ( FIG.  3   ) via the power lead  146  ( FIG.  3   ). The analog switch  254  may be provided for restarting, adjusting, or otherwise interfacing with the pollution monitor. The primary battery holder  256  and secondary battery connector  258  may be provided for receiving a power source. In one configuration, the secondary battery connector  258  may receive a primary (non-rechargeable) battery. For example, the secondary battery connector  258  may receive a large battery such as an absorbed glass mat lead-acid battery or it may receive a coin cell battery depending on the particular application for the pollution monitor. 
     With reference to  FIG.  22    illustrating the temperature/humidity sensor  260  and microphone  262 , the temperature/humidity sensor  260  may be any of a number of types of sensors. In one illustrative example, the temperature/humidity sensor  260  may be a temperature/humidity sensor with multiple functions and various interfaces (I2C, analog voltage output) that operates across a wide operating voltage range (2.15 to 5.5 V). The temperature/humidity sensor  260  may include enhanced signal processing, distinctive and user-selectable I2C addresses, an alert mode with programmable humidity and temperature limits, and communication speeds of up to 1 MHz. In one illustrative example the temperature/humidity sensor  260  may be a the Sensirion SHT31-D sensor with ±2% relative humidity and ±0.3° C. temperature accuracy. With continued reference to  FIG.  22   , the microphone  262  may be configured as a micro-sized I2S output microphone that can be used to digital record audio and be sent to an MCU/SOC in digital format without the need for any CODEC or additional hardware typically needed with an analog microphone. Output from the microphone  262  can be directly connected via I2S port and does not require any additional components such as a codec to provide digital audio. The microphone  262  may be configured to directly or indirectly report sound level, sound frequency, and/or spectrum density. One illustrative example of a microphone is the Sensor Maestros MIC-SPH0645LM4H-B. 
     With reference to  FIG.  23   , the metrological connector  264  may be connected to an external device capable of reporting environment conditions (weather) such as wind speed, wind direction, temperature, humidity, dew point, rain level, etc. In one configuration, the metrological connector  264  receives a device that presents three weather measurement: wind speed, wind direction and rainfall. The rain gauge may be a self-emptying bucket-type rain gauge which activates a momentary button closure for each 0.011 inches of rain that are collected. The anemometer (wind speed meter) may encode the wind speed by simply closing a switch with each rotation. And, a wind vane may report wind direction as a voltage which is produced by the combination of resistors inside the sensor. One example of this device is Sparkfun SEN-08942. 
     With continued reference to  FIG.  23   , the first pollution sensor  266  may be a methane sensor such as an infrared combustible gas sensor having an integrated system and includes mirror optical system, photodiode and LED, signal amplifiers, microcontroller, current driver of the infrared LED, UART interface signal generator and forming voltage supply unit. The sensor&#39;s microcontroller performs storage of unique sensor calibration constants, processing of measurement results and concentration of measured gas, and information exchange. One illustrative version of the first pollution sensor  266  operates according to a principle based on NDIR technology, i.e. on selective infrared radiation absorption by gas molecules. Infrared radiation from LED permeates through a measuring diffusion-type gas cell and arrives on signal and reference photodetectors, one of which detects radiation only in the wavelength range of infrared radiation absorbed by gases, while the other one detects radiation only in the wavelength range of 3.5 to 3.7 μm. Gas flowing through the cell absorbs the radiation of the operating wavelength and does not affect the radiation of the reference wavelength. One example of a sensor is the MIPEX-04 by Mipex Technology. 
     With reference to  FIG.  24   , the physical sample connector  272  may be a telecommunications registered jack commonly used in the telecommunications industry such as, for example, a typical RJ45 connector accessible from the outside of the pollution monitor. Other features are illustrated such as fiducials and mounting holes. 
     With reference to  FIG.  25   , the location module  274  and location antenna connector  276  may be any of a variety of types of location devices, such as those using the global positioning system. Some examples of location modules are application specific and have an antenna integrated on the device that utilize technology to calculate and predict location satellite orbits automatically using the ephemeris data stored in internal RAM memory to enable the location module to quickly report a location without consuming much power. If the integrated antenna is insufficient for capturing a satellite(s) location, an external antenna may be used (via the location antenna connector  276 ). In one illustrative example, the location module  274  is a Quectel L80 GPS. As used herein, the term ‘geolocation’ is the identification or estimation of the real-world geographic location of an object. In its simplest form, geolocation may include generation of a set of geographic coordinates and is closely related to the use of existing positioning systems or simply as a street address. The word ‘geolocation’ may refer to the latitude and longitude coordinates of a particular location described by the standardized real-time locating system standard ISO/IEC 19762-5:2008. 
     With reference to  FIG.  26   , the communications module  278  and communications antenna connector  280  may be any of a variety of communication devices. In one embodiment, the communications module may be configured to communicate with other pollution monitors (e.g. by mesh, WiFi, cellular, satellite, etc.). The communications module  278  of the electronics package  150  may be any of a variety of communications devices ranging from infrared communications components (IR LEDs and photodetectors) to radio frequency communications components. While any of an almost infinitely large variety of communications protocols may be implemented, some particularly useful examples include Bluetooth, LORA, SIGFOX, SIGBE, satellite communications, particle.io, radio, TLE, CDMA, GSM, etc. If provided with the communications module  278  configured as a Particle.io device, the hardware may include a 120 Mhz ARM Cortex M3 microcontroller and a Wi-Fi chip. In one embodiment, the electronics package  150  may be updated via over-the-air firmware updates utilizing a protocol. 
     With reference to  FIG.  27   , the first expansion connector  282 , the second expansion connector  284 , and the third expansion connector  286  may be useful for future development/functionality. In one example, the first expansion connector  282  may be interfaced with the transmit and receive lines of the first pollution sensor  266  (e.g. the MIPEX-04 sensor). Further, the second expansion connector  284  may be interfaced with other pollution sensor if so desired. 
     With reference to  FIG.  28   , the fourth pollution sensor  288  and boost converter  290  may be provided for accurately determining particular matter in the atmosphere. For example, the fourth pollution sensor  288  may be configured as a sensor operating on the principle on laser scattering uses an innovative contamination-resistance technology. In one example, the fourth pollution sensor  288  may be configured as another Sensirion SPS30 to augment the other sensor provided in duplicity for accuracy, redundancy or life-span extension. If configured with a boost converter  290 , the output voltage presented to a sensor (e.g. the fourth pollution sensor  288 ) may be accurate to the point that anomalies in the sensors output are nearly eliminated. On example of a boost converter  290  is Texas Instrument&#39;s TPS61240. 
     With reference to  FIG.  29   , the power switch  292  may be provided to power sensors (e.g. pollution sensors) or other modules of the electronics package  150  (e.g. location module). One example of the power switch  292  is Texas Instruments TPS2052B. 
     With reference to  FIG.  30   , the voltage regulator  294 , the first pollution sensor  266 , and the signal translator  296  may be provided for cooperating to measure a pollutant that is in the atmosphere. In some instances, the first pollution sensor  266  requires an accurate voltage and therefore the voltage regulator  294  may be utilized for improving the pollution signal emitted by the first pollution sensor  266 . In an effort to further improve signal accuracy (and in some cases response), the signal translator  296  may be utilized to accelerate signal handling. The signal translator  296  may be a device that includes a dual bidirectional I2C and SMBus voltage-level translator with an enable input allowing bidirectional voltage translations between 1.2 V and 5 V, without the use of a direction pin. The low ON-state resistance of the switch allows connections to be made with minimal propagation delay. In one example, the voltage regulator  294  may be configured as the Diodes Incorporated AP2127K. In another example, the first pollution sensor  266  may be the Sensiron SGPC3. In another example, the signal translator  296  may be the Texas Instrument PCA9306. 
     With reference to  FIG.  31   , the second pollution sensor  268  may provide pollution detection and reporting pollution. In one example, the second pollution sensor  268  may be a low-power digital gas sensor solution which integrates a gas sensor solution for detecting low levels of VOCs. The second pollution sensor  268  may include a microcontroller unit (MCU) and an Analog-to-Digital (A/D) converter to monitor the local environment and provide an indication air pollution via an equivalent CO2 or total VoC output over a standard I2C digital interface. In one example, the second pollution sensor  268  may be an AMS CCS81. 
     Having described various embodiments of apparatus for reducing fugitive emissions at oil facilities, various illustrative methods of reducing fugitive gas emissions and other features will now be presented. 
     With reference to  FIG.  32    illustrating a top plan view of an oil facility experiencing a leak (sometimes referred to as an emissions source  400 ), the oil facility is monitored by at least one pollution monitor (e.g.  102 ,  104 ,  106 , or  108 ). The illustrated example utilizes four pollution monitors: the pollution monitor  102  positioned at a West boundary  402  of the monitored area  90 ; the pollution monitor  104  positioned at a North boundary  404  of the monitored area  90 ; the pollution monitor  106  positioned at an East boundary  406  of the monitored area  90 ; and, the pollution monitor  108  is positioned at a South boundary  408  of the monitored area  90 . Wind  410  (illustrated as directional arrows) is a mass of ambient air moving from the West towards the East. This idealized illustration is a snapshot in time, and it is understood that wind is rarely unidirectional as illustrated—however this illustration conveys some principles of the present disclosure. As the wind  410  moves into the monitored area  90  at the West boundary  402 , the pollution monitor  102  reads a property of the ambient air via the pollution sensor  202  in the electronics package  150  (both in  FIG.  6   ). As the wind  410  continues across the monitored area  90 , any matter added to the wind  410  increases the pollution. For example, if the emissions source  400  is leaking hydrocarbons in the atmosphere, the wind  410  will ‘gain’ in hydrocarbons. This gain may be detected by the system that utilizes pollution monitor  106  and the pollution sensor  202  of the electronics package  150  (both in  FIG.  6   ). 
     With continued reference to  FIG.  32   , readings from the individual pollution sensor  202  in the pollution monitors  102  and  106  may be interpreted by the logic control system  190  ( FIG.  8   ) and may be transmitted to an internet-attached web hosting server  420  via the communications module  204  ( FIG.  15   ) and a communications tower  422 . When the sensor readings are compared (either at a local-level inside one or more of the pollution monitors, at/on the internet-attached web hosting server  420 , etc.), the emissions source  400  is detected and located. With this detection and/or location, an operator (or other interested party) of the monitored area  90  can be notified for any of a variety of actions including, but not limited to, opening a troubleshooting ticket, adding field service to an upcoming maintenance list, initiating a truck-roll to the monitored area  90 , or a variety of other actions depending on predetermined thresholds and/or remedy actions. 
     While  FIG.  32    shows the wind  410  moving from the West to the East (i.e. Westerly wind), in reality the wind moves from the West, to the North, to the South, and generally in all directions. Therefore, the present oil facility  100  is configured to receive data from the various pollution monitor  102 ,  104 ,  106 ,  108  and to process (e.g. average or otherwise interpret/process) the results to increase confidence of the findings. The utility of the clock module  224  ( FIG.  15   ) may be that each snapshot of data is timestamped. The timestamped data may be utilized to accurately assess the operation of the event and to clearly know conditions inside and around the monitored area  90 . 
     With reference to  FIG.  33    illustrating a graph of sensor outputs from a plurality of pollution monitors (e.g.  102 ,  104 ,  106 ,  108 ), the graph shows one particular pollution as hydrocarbons in parts per million (PPM) graphed against time. For example, if the same event from the description of  FIG.  32    is represented on the present graph, the outputs from pollution monitor  106  will spike during presence of the emissions source  400  ( FIG.  32   ). Once the emissions source  400  terminates (either by repair or other change), the reading drops to the ambient level as illustrated. 
     In one illustrative configuration, a method for reporting atmospheric pollution may include steps to perform the reporting. In a first step, a first pollution monitor  102  and a second pollution monitor  106  may be installed in (or around) a monitored area  90 . In a second step, the pollution levels present (and sensed) at the first pollution monitor  102  and the second pollution monitor  106  are sensed and compared. During normal operation of the two different pollution monitors,  102 ,  106 , the pollution sensor  202  ( FIG.  6   ) in each pollution monitor  102 ,  106  sense and report a presence of matter such as hydrocarbons in parts per million. During a third step, the readings of atmospheric pollution originating at the oil facility are reported. A leak may be detected in a number of ways such as: a predetermined threshold is reached (and the confidence is high that there is a valid reading indicating presence of the emissions source  400 ); or, exceeding a threshold (differential concentration) and occurring over a duration (how long has the leak been going on) as criteria for generating a report (alert via SMS or email) of a possible leak condition. It is worth noting that as the wind direction changes during a leak event and therefore the reading of a sensor may decrease, but the larger system may continue to treat the leak event as continuous for the sake of meeting the ‘duration’ criteria. Differentiating between normal field operations and actionable emission events may require sophisticated algorithms (e.g. conventional statistical analysis and/or more nuanced applications of machine learning). These algorithms may be updated before deployment or during operation through coordinating with field operations facilities to guide the system by integrating site service records into the emissions data stream. Once a leak is determined, the reporting may commence (e.g. through an alert via SMS, Email, or other communications platform). During the reporting step, the operator of the monitored area  90  may be notified for any of a variety of actions including, but not limited to, opening a troubleshooting ticket, adding field service to an upcoming maintenance list, initiating a truck-roll to the monitored area  90 , or a variety of other actions depending on predetermined thresholds and/or remedy actions. In order to reduce false-positive events, the readings from the pollution monitors  102 ,  104 ,  106 ,  108  may be average-adjusted to compensate for initial discrepancies in the pollution sensor  202  readings or differences that evolve over time due to unique performance characteristics that may not be accounted for during the initial production or qualification of each individual pollution sensor  202 . For example, each individual pollution sensor  202  from each of the pollution monitors  102 ,  104 ,  106 ,  108  can be compared to establish what is the baseline reading for each pollution sensor  202 . This comparison may, for example, occur via peer-to-peer communication via the communications module  204  or in the internet-attached web hosting server  420 . 
     With reference to  FIG.  34    illustrating a geographic area and a rural oil facility, the rural oil facility may be relatively far (e.g. 100 miles) from a home-location for a repair technician. Therefore, when a leak (e.g. holding tank  96  may have a faulty valve, for example) is detected and reported, a vehicle  500  may be deployed to carry a technician  502  and a mobile device  504  to repair the leak at the rural oil facility. In this illustration, the pollution monitor  106  (or other parts of the system) may emit a signal indicating elevated levels of a pollutant. The signal representing an elevated level is checked against a set of rules to determine if there is likely a leak. If the rules are met and therefore there is likely a leak, the system requests/instructs that a leak be repaired. In doing so, the system may send the repair instruction to the mobile device  504 , thereby informing the technician  502  about the leak and requesting the technician  502  activate the vehicle  500  for travelling to the oil facility  100 . 
     In one illustrative configuration, a method for activating a truck to move a technician to a rural oil facility as part of a process for repairing a leak, the pollution monitor is deployed at the oil facility and activated to monitor a signal representing atmospheric presence of at least one component of natural gas. In one illustrative embodiment, the sensor that produces this signal may include a hotplate and metal oxide semiconductor that changes resistance in presence of the component of natural gas. Once the signal is received, it is compared to a set of rules. The rules may be as elementary as crossing a threshold, or they may be more complicated and derived over time from machine automation (sometimes referred to as artificial intelligence, AI). This comparison may happen onboard the pollution monitor  106  or at a remote location (e.g. the internet/web hosting server  420 ) after the signal data is sent wirelessly. After comparing, the instruction to repair may be invoked. While many different repair instructions/actions may take place, one repair might require a vehicle to be activated to bring a repair technician to the rural oil facility to repair the leak. It is noted that any of the activities herein that are manual may have an underlying machine instruction leading up to the manual activity; this machine instruction may come in the form of a ticket, job order, text message, email, report, etc. indicating that the manual activity is to be implemented. 
     With reference to  FIG.  35    illustrating a top plan view of an oil facility with a pollution monitor system, sound emitting from a leak travels to pollution monitors of the pollution monitor system. An emissions source  400  emits noise as it leaks into the atmosphere due to its relatively high energy level (e.g. high heat and/or pressure). As this noise travels from the emissions source  400  to the pollution monitors (e.g.  102 ,  104 ,  106 ,  108 ), it is absorbed by various objects or otherwise dissipated into the environment. Therefore, the sound level of this noise is represented by concentric rings from the emissions source  400 . To be clear, the noise level immediately adjacent to the emissions source  400  may be relatively high (e.g. 110 db) and taper off at locations away from the emissions source  400 . When the emissions source  400  is located at different distances from the pollution monitors, the sound levels measured by the pollution monitors vary. As illustrated, the level of sound received at the pollution monitor  104  are different than the level of sound received at the pollution monitor  108 . As illustrated, the noise level at pollution monitor  106  is higher than the noise level at pollution monitor  102 . Through a process of vectoring, the location of emissions source  400  can be determined. As used herein, the term ‘vectoring’ may refer to acoustic source localization of a sound source given measurements of the sound emitting from an object/location (e.g. emissions source  400 ). The sound can be described using physical quantities (e.g. sound pressure and particle velocity). By measuring these properties it may be possible to obtain a source direction. Sound pressure (i.e. sound level) may be measured using a microphone having an omnidirectional polar pattern (sensitivity is independent of the direction of the sound). When a number of microphones are used, it is possible to locate a sound source through comparing sensed sound levels. 
     The above description of apparatus and methods are just illustrative embodiments provided for descriptive purposes. Other embodiments have been contemplated, such as the following alternatives. 
     In one alternative configuration, a method for transferring stored data representing pollution levels from a rural oil facility to a data center movement of a truck and transfer of the data via a communications protocol. This method for transferring data from a rural oil facility to a data center may commence by provisioning a pollution monitor at the rural oil facility. This provisioning may, for example, include driving a vertical object (e.g. a T-post) into the ground and attaching the insulating body  110  with the electronics package  150  to the t-post. It may place a pollution sensor in electrical communication with the electronics assembly  150  wherein the pollution sensor is configured to report a signal representing atmospheric presence of at least one component of natural gas. In the present description, the rural location may be ‘off-network’ whereby the wireless communication may be difficult if not impossible (for example, cellular data might not be available or too costly). At any rate, the signal data can be stored until a mobile device (also referred to herein as an electronic device) arrives at the oil facility. Once the mobile device is received at the oil facility via a vehicle, the stored signal can be transferred to the mobile device. In due course, the technician drives with the mobile device to a connected environment (e.g. a location where cellular data is present, or where a WiFi signal exists). At this point, the signal data can be transferred via at least one communication protocol. The method may be useful for locations where a communication protocol is difficult or impossible, but still provides a method for removing data from the oil facility. 
     In another alternative configuration, a method for locating a leak at an oil facility by vectoring the sound levels originating at the leak may begin by provisioning at least three pollution monitors. Each of the pollution monitors may be provided with a sound module (e.g. a microphone as described herein) configured to output a signal representative of the level of sound it is exposed to. The signals are sent from a pollution monitor and received (e.g. by one pollution monitor, a shared resource, or an offsite computer). The signals are used to locate the leak by comparing the signals in a process referred to as vectoring. In this process, the relative strength of a signal is utilized to triangulate in on the location of the emissions source  400 . 
     In another alternative configuration, a method for identifying a leak at an oil facility by analyzing signal frequency may begin by provisioning a pollution monitor with a sound meter configured to output a frequency signal. Once the signal is sent and received, it is analyzed against a set of frequencies representing sounds emitting from leaking components. In an oil facility, there are a number of devices that have unique properties. Some of these devices are made of ‘lively’ materials (e.g. brass) ringing at a high frequency while others are made of relatively ‘dead’ materials (e.g. ductile iron). Therefore, when one of these devices is experiencing a leak nearby or, in one example, from the device, they emit a sound with a unique signature frequency. For example, a leaking solenoid valve may emit a loud screeching noise while a section of leaking pipe may emit a bass-like rumble. Ultimately, a determination of the leaking component may be made based on the analysis of the frequency of the sound. This may help to repair technician to be properly provisioned with repair materials and/or tools when they arrive at the oil facility to repair the leaking device. 
     In another alternative configuration, a method of locating a leak by comparing phase-arrival of signal may begin by provisioning a plurality of pollution monitors. Sound meters are included with pollution monitors that are capable to output a signal that represents arrival of a phase of the soundwave. The signal representing the phase arrival are received from the pollution monitors and compared to determine the location of a leak. As processors and sound meters improve, their sensitivity and speed may enable timely detection of phase arrival times. In accurately comparing arrival of a phase of sound, it may be possible to determine the distance and relative location of a sound source (e.g. a leak). 
     In another alternative configuration illustrated in  FIG.  36    showing a top plan view of an oil facility  600  configured with a pollution monitoring system  602 , a plurality of pollution monitors may be deployed at the oil facility  600  surrounding a centroid  604 . For example, a first pollution monitor  610  may generally be located at a North-Northwest (N-NW) location relative to the centroid  604 . A second pollution monitor  612  may be located at a Northwest (NW) location relatively to the centroid  604 . A third pollution monitor  614  may be located at a North location relatively to the centroid  604 . A fourth pollution monitor  616  may be located at a Northeast (NE) location relatively to the centroid  604 . A replacement pollution monitor  618  may be located at the Northeast (NE) location relatively to the centroid  604 . Additional pollution monitors may be positioned as illustrated relative to the centroid  604 . In some a process that will be described herein, the pollution monitors may need to be replaced occasionally. For example, the fourth pollution monitor  616  may be hit by a service vehicle or for some other reason require replacement. The fourth pollution monitor  616  may be located at a first bearing  620  and a first distance  622  from the centroid  604 . The first bearing  620  may be defined as an angle relative to due North, for example, as illustrated. The first distance  622  is a unit of measure from the centroid  604 . When (or earlier, e.g. during initial provisioning) the damaged fourth pollution monitor  616  is replaced, this first bearing  620  and first distance  622  are noted. When the replacement pollution monitor  618  is deployed, it may not be necessary to position it exactly at the same first bearing  620  and first distance  622 . In one example, the replacement pollution monitor  618  may be located at a second bearing  624  and a second distance  626  that is different than the first bearing  620  and first distance  622 , respectively. However, for the purposes of monitoring the oil facility  600 , the replacement pollution monitor  618  can be referred to as the Northeast location when provisioned at the second bearing  624  and the second distance  626 . 
     In another alternative configuration, a method of provisioning a replacement pollution monitor at an oil facility may begin by noting an original location of a first pollution monitor. During the provisioning of a second pollution monitor, a bearing and distance of the second pollution monitor may be recorded. The bearing and distance of the second pollution may be compared to the first location monitor (e.g. its bearing and distance from a centroid). If the second pollution monitors bearing and distance comply with a predetermined set of rules, the second pollution monitor receive the location identifier of the first pollution monitor, and the first pollution monitor may be decommissioned. Even though the second pollution monitor is located at a slightly different location, it can be provisioned into the pollution monitoring system  602  having the same location identifier as the first pollution monitor. It has been found that a certain amount of tolerance is useful and/or required when replacing a pollution monitor. This maintains the database legacy and forward looking data rules and actions that rely on data from the first pollution monitor and any of its replacements. 
     In another alternative configuration in  FIG.  37    showing a perspective view of a pollution monitor  650  configured with an optional physical sampling system  652  configured to capture a physical sample (e.g. air sample  212 , soil sample  214 , water sample  216 ,  FIG.  15   ). The physical sampling system  652  may be configured to sample air via any of a variety of sampling devices known. For example, U.S. Pat. No. 3,866,474 to Hasselman describes a system in which a sample and an inert gas are drawn into a sample bag within a hermetically sealed container. U.S. Pat. No. 3,965,946 to D&#39;Alo describes improvements to an outer container for sample air. U.S. Pat. No. 5,437,201 to Krueger describes a method of repeatedly purging the sampling bag within the outer container. U.S. Pat. No. 5,714,696 to Yemans describes a system for sampling air. U.S. Pat. No. 6,338,282 to Gilbert describes an apparatus for collection air. U.S. Pat. No. 6,993,985 to Srebro describes using the apparatus combined in single device yet connected to external vacuum source. U.S. Pat. No. 4,546,659 to Gill et al. describes a small (10 ml) envelope for the collection of atmospheric air samples for subsequent analysis. All of the above patents are specifically incorporated by references for all they disclose. In one illustrative configuration, the physical sampling system  652  includes a collection device (e.g. summa canister  654 ) and an actuator (e.g. solenoid valve  656 ). The summa canister  654  may be a canister capable of being held at a vacuum or otherwise intaking a sample of air. In one example, the summa canister  654  is deployed with a vacuum contained therein. When the solenoid valve  656  is activated, a portion of atmosphere (air) is pulled into the summa canister  654 . The action of the solenoid valve  656  may be remotely controlled or as illustrated connected to the pollution monitor  650  via a cable  658 . From time to time, or during a leak event, the pollution monitor  650  may instruct the capture of a physical sample. In a similar manner, the physical sampling system  652  may be configured to capture and preserve a sample of water, a sample of fluid from the oil facility, a sample of soil, or other material as required. 
     In another alternative configuration, a method of collecting a physical sample may begin by provisioning a pollution monitor. Before provisioning, or at some point thereafter, at least one rule is established for invoking a sampling event. During regular operation of the atmosphere, the pollution monitor may be utilized to monitor for breach of the rule. If the rule is breached/met, the pollution monitor invokes to sample. The sample is captured with the physical sample and a location and/or time is attached to the sample. In some implementations, the physical sampling system  652  may be utilized as a one-time event. Alternatively, the physical sampling system  652  may draw in small samples over a period of time to determine a time-based average of pollution in the air. At a later point and (most likely) a different location, further analysis of the sampled air may help to identify the constituents of the air. For example, if the air contains a lot of propane, it its source is likely an oil and natural gas (O&amp;NG) facility like a well or storage tank. Alternatively, if the air consists primarily of refined gasoline with additives, there might be a foul-running generator nearby that is simply emitting unspent gas as exhaust. Therefore, the collection of samples are useful to classify the source through a detailed analysis. With this approach, external emissions sources may be disregarded without requiring laboratory grade analysis. 
     In another alternative configuration, a method of pricing natural gas may begin by monitoring an oil facility for a leak. Occasional leaks at the oil facility occur and timely and reliable repair are validated. If the repair is made timely and reliably, a clean certificate may be attached to a unit of natural gas. Sites with the fewest emissions may command the highest level of certification. This unit of natural gas with its attached clean certificate may be sold. Certain buyers of energy desire to have natural gas (or other extracted matter) that is sourced with minimal impact on the environment. Therefore, the market values certified clean matter at a higher rate than non-certified matter. This unit of natural gas with a clean certificate may create a new class of commodity with a premium price and/or a desirable market acceptance. Data integrity, security, and authentication may be of paramount importance to the accurate pricing of this commodity and methods may be applied to ensure that there is immutable, auditable, and complete ledger of the low carbon footprint of this product. 
     In another alternative configuration, a method of reporting quality of service of a repair at an oil facility may begin by installing a plurality of pollution monitors around an oil facility. A boundary may be established by connecting locations of the plurality of pollution monitors to define an on-site zone and an off-site zone. The pollution monitors may be used to detect a leak in the on-site zone; and, a technician located in the off-site zone may be moved to the on-site zone. The technician may repair the leak. The time to repair the leak may be noted; and, long-term effectiveness of the repair may be calculated. The time and effectiveness of the repair may be reported. The time and effectiveness may be used, for example, to confirm suitability of the repair technician. 
     In another alternative configuration, a method of subsidizing (at least some of) the purchase price of natural gas (by transacting a carbon credit), the process begins by baselining similar oil facilities to determine the typical emissions. The oil facility is monitored for a leak; and, all leaks are responded to. The response to leaks is validated. A carbon credit is attached to a unit of natural gas. The carbon credit may be transacted to a first buyer; and, the unit of natural gas may be transacted to a second buyer. The market has established frameworks for transacting (e.g. selling) matter with carbon credits attached thereto. The buyer of carbon credit containing units of natural gas maybe one user, or the buyer may opt to only purchase either the carbon credit or the unit of natural gas. 
     In another alternative configuration, a method of instructing another party to respond to a leak at an oil facility to cause transaction of a carbon credit, the process may begin by baselining similar oil facilities to determine the typical emissions. The oil facility is monitored for a leak; and, all leaks are responded to by another party. The response to leaks is validated. A carbon credit is attached to a unit of natural gas. The carbon credit may be transacted to a first buyer; and, the unit of natural gas may be transacted to a second buyer. Oil exploration, extraction, distribution, and processing is complicated and involves a number of parties. While the present illustrative examples attempt to narrow activities to the actions of one entity, various entities might perform actions. These actions may be taken on behalf of, or as instructed by, one party (e.g. the end consumer, the retailer, the producer, etc.). 
     In another alternative configuration, a method of confirming presence of a vehicle moving across an area populated with a plurality of pollution monitor may begin by providing a plurality of pollution monitors. The pollution monitors may monitor pollution sensors; and, when different pollution monitors validate identical atmosphere levels, a mobile emission source is identified. The presence of a mobile emission source is confirmed. Occasionally, a mobile emissions source such as a tractor may emit a large amount of hydrocarbons. This mobile emission source may cause false-positive reports of a leak at the oil facility. Therefore, identification of mobile emissions sources may be useful in confirming valid leaks. 
     In another alternative configuration, a method of validating a pollution event by analyzing a plurality of sensors and/or monitors for at least two breaches may begin with provisioning a pollution monitor having a variety of sensors. The presence of a leak may be validated by analyzing signals from the sensors by comparing signals from two or more sensors. While sensor and their associated signals may indicate leak events, it is useful to validate the leak before instructing to initiate actions (e.g. deploying a technician to the monitored area to repair a leak). Therefore, monitoring a plurality of sensors is useful. 
     In another alternative configuration, a method of adjusting communication frequency based on power budget may begin by monitoring the power input. The power stored in a battery is monitored. The telemetry is adjusted based on budget, actual and forecast power. The telemetry activities of a pollution monitor require a large amount of power, but the amount of data does not substantially change the amount of power required to report. Therefore, if charging conditions are diminished (e.g. low solar-resource days), the frequency of reporting can be adjusted. 
     In another alternative configuration, with reference to  FIGS.  38  and  39    illustrating an information display in data modality and map modality, respectively, data from the pollution monitors may be configured as a website page served on the internet. Information received by the internet-attached web hosting server  420  ( FIG.  32   ) via the communications tower  422  ( FIG.  32   ) and the communications module  204  ( FIG.  7   ) may be processed without any human interaction or influence. Alternatively, the data may be presented on a device, a webpage, a database, or any of a variety of other methods for receiving data. In one example, the data of one or more pollution monitors (e.g.  102 ) may be presented on a webpage that is updating at an interval. The updating interval may be so fast as to essentially be ‘real time’ or it may be every few hours (in one example it may be updated yearly). IoT data frequently needs some form of real-time dashboard. The present system utilizes a (custom-built or third-party) platform for illustrating the data in both a Data Modality ( FIG.  38   ) and a Map Modality ( FIG.  39   ). Creating and/or using these platforms facilitates rapid development and experimentation, for example, the granularity of data on the data modality of  FIG.  38    can be adjusted. The data shown in the data modality ( FIG.  38   ) may be at least one of the following: min, max, average pollution level (e.g. VoC), and time-series data that has been captured and/or processed by the electronics package  150 . The data may be presented as realtime data, as spot-presented data, as summarized data, as max reading(s), as minimum reading(s) and/or as average data. Depending on the type of installation and required performance of the system, this data may be altered inside the electronics package  150 , or the system (specifically one of the pollution monitors), or the internet-attached web hosting server  420 , or on a local machine (not shown). In one embodiment, real time charts showing min, max, and average readings are provided in order to differentiate pollution monitors across an oil facility in order to monitor/watch for and analyze different readings. The map modality of  FIG.  39    illustrates regional geospatial displays it may be appropriate to show individual devices. Data may be aggregated analyzed and summarized into a visual representation that enables the user to discern locations of interest. Drilling down from regional displays to more local geospatial areas may result in a different representation and a more fine-grained representation of the individual device data. 
     In another illustrative configuration, a method of communicating with property owners near an installation of a pollution monitor may begin by informing the neighboring property owners. The pollution monitor may be showed to at least one of the property owners. A link may be shared for public viewing of signals of the pollution monitor. The transparency of data from the method of communicating helps to avoid misunderstandings about the source of emissions. 
     In another alternative configuration, with reference to  FIG.  40    illustrating a perspective view of one configuration of a pollution monitor  670 , the pollution monitor  670  may be configured with an optional meteorological system (e.g. a wind sensor). The pollution monitor  670  may be provided with an air conveyance system  680 . The air conveyance system  680  may include a tube  682  defining a sensor end  684  and an oppositely disposed collection end  688 . The tube sensor end  684  may be attached to the electronics package housing  160  at the sensor opening  184  ( FIG.  6   ). The tube collection end  688  may be positioned where the sampling should occur, for example as-illustrated on top of a body of water, or alternatively, down a borehole, on the top of a tank, inside a house, or wherever the ambient air may be monitored. The air conveyance system  680  may be further provided with a fan  690  fitted inline with the tube  682  for ensuring that the ambient air travels from the collection end  688  to the sensor end  684  of the tube  682 . The fan  690  operates according to a set of predetermined inputs, intervals, or otherwise instructed by pre-programming, spot-programming or acquired intelligence. In many situations, air to be collected is located at a difficult location (e.g. the surface of a river, inside a holding tank, in a cave, underground in a drainage vault, etc.). Often these difficult locations are subject to temporary flooding or are close to livestock or are prone to vandalism/theft. Therefore, providing a flowpath and conveyance from the difficult location to the environmental sensor is required. The hose  682  with a forced displacement device (e.g. the fan  690 ) may enable difficult locations to be monitored. 
     In another alternative configuration also shown in  FIG.  40   , the pollution monitor  670  may be provided with a meteorological module  700  configured to monitor any of a variety of environmental conditions. In one example, the meteorological module  700  may measure the humidity and/or the temperature of the air presented thereto. The meteorological module  700  may include a wind sensor  702  capable of measuring the speed and direction of the wind. The meteorological module  700  may further include features for measuring precipitation (rain, snow) or other conditions. 
     In another alternative configuration also shown in  FIG.  40   , the pollution monitor  670  may be provided with features for avoiding birds from interfering with the solar charging capabilities. For example, the pollution monitor  670  may be configured with a spike strip  710  attached to the top of the pollution monitor  670  as illustrated. 
     In another alternative configuration also shown in  FIG.  40   , the pollution monitor  670  may be configured with additional solar panels such as a second panel  720  and a third panel  730 . The second panel  720  may be attached to a side of the pollution monitor  670  and the third panel  730  may be attached to the front of the pollution monitor  670 . 
     In another alternative configuration shown in  FIG.  32   , the oil facility  100  may include four individual pollution monitors (e.g.  102 ,  104 ,  106 ,  108 ) or it may be provided with a relatively large number of pollution monitors (e.g.  280 ,  282 ,  284 ,  286 ). Regardless of the number of individual pollution monitors, they may communicate peer-to-peer (e.g. via a wireless mesh cellular network, via a proprietary network, or even via direct satellite transmission) or via the communications tower  422  and internet-attached web hosting server  420  via each environmental monitor system communications module  204  ( FIG.  8   ). A few of the individual pollution monitors can be a centered cluster and further-away systems can be utilized to normalize or otherwise process data obtained by the systems. In a similar manner, a large string of data for each pollution monitor can be compared to as-measured readings in an effort to reduce false-positive events. 
     In another alternative configuration also shown in  FIG.  32   , the plurality of pollution monitors ( 102 ,  104 ,  106 ,  108 ,  280 ,  282 ,  284 ,  286 ) may communicate to time-average their baseline readings of the pollution sensor  202 . Because the wind  410  is always changing direction and events are few and far between, over time, the readings of various pollution monitors can be evaluated (either manually or statistically) to arrive at an ‘average’ steady-state reading. 
     In another alternative configuration also shown in  FIG.  32   , the oil facility  100  houses the holding tanks  96  which may emit fluid (either gas or liquid) as the emissions source  400 . If the emissions is hydrocarbons sourced from underground, the hydrocarbons may include many types of compounds. While methane is one particularly environment-degrading emissions, it is often emitted along with volatile organic compounds. In some, but not all, situations it is possible to estimate/measure methane emissions by measuring/sensing VOCs. As described herein, various sensors are capable of measuring VOCs such as micro hot-plate sensors. By sensing VOCs, the emission of methane can be estimated. The direct measurement of methane is relatively complex because methane is somewhat lighter than air, may be difficult to detect by nearly ground-level devices. 
     In another alternative configuration also shown in  FIG.  32   , the individual pollution monitors ( 102 ,  104 ,  106 ,  108 ,  280 ,  282 ,  284 ,  286 ) can communicate directly in a peer-to-peer manner via their individual LAN communications modules  208  ( FIG.  8   ) where one pollution monitor may (or may not) communicate data to the internet-attached web hosting server  420  via the WAN communications module  210  of the pollution sensor  202 . If implemented, this greatly reduces the power requirements of the oil facility  100  because communicating to nearby devices is substantially more energy efficient then communicating to distant devices. 
     In another alternative configuration, the pollution sensors may be configured with other and/or additional pollution sensors. For example, other pollution sensors cable of monitoring and/or reporting methane, particulates, volatile organic compound(s), etc. may be utilized. The pollution sensors may be any of a large variety of sensors, but in one configuration, the sensor module may be capable of sensing emissions from an oil extraction, storage, delivery, processing, and/or distribution component or system. Once such sensor is a volatile organic compound (VoC) sensor. Illustrative examples of sensors capable of sensing VOCs are temperature-controlled micro-hotplate devices such as the SGPC3 Sensirion Gas Platform made by Sensirion, www.sensirion.com. Another type of VOC sensor is an ultra-low power digital gas sensor for monitoring air quality that is manufactured by AMS and sold as model CCS811. The CCS811 is a digital gas sensor that integrates a metal oxide gas sensor to detect a wide range of VOCs using a micro-hotplate (also referred to herein as simply having a ‘hotplate’). In yet another illustrative variant, pollution sensors may be a light-gate sensor wherein a light source creates light that is projected through air containing a gas (e.g. VOC such as Methane, Hexane, Toluene, Propane, Benzine, etc.) and received by a photodetector (e.g. ccd or cmos). The light received by the photodetector is processed and analyzed to determine constituents of the air through which the light passed. All of the sensors either present analog or digital information that indicates the presence of the component which it is intended to sense. In one example, the data is presented as binary data according to the I2C protocol well documented and known to those skilled in the art. This data is either processed by the electronics package  150  or transmitted to the cloud via the communications module  204  for later processing. 
     In another alternative configuration best illustrated in  FIG.  15    illustrating one embodiment of a schematic diagram of optional power management devices of a pollution monitor (e.g. power switching, watchdog, etc), the electronics package  150  consumes power. Power may be provided by a grid-tied connection (not shown) or a battery  198 . In most applications, the oil facility  100  is distant from the national grid and therefore the battery  198  is utilized and it is charged by the solar panel  140  ( FIG.  3   ). With continued reference to  FIG.  15   , the electronics package  150  is, typically, capable of budgeting the daily power created by the solar panel  140  and stored in the battery  198 . In typical mid-summer days, the sun&#39;s intensity causes excess power to be generated and operation can occur relatively frequently and with little regard for the amount of power consumed by the electronics package  150 . Alternatively, in the middle of winter during a long period of foul weather, the electronics package  150  may need to reduce its overall power demands to compensate for the relatively low daily-power crated by the solar panel  140 . The sampling cycle may be reduced during lower-power days (or periods) and/or the reporting of the data via the communications module  204  may be reduced as telemetry usually requires high amounts of power. In other words, the electronics package  150  and various components may be preprogrammed, spot-programmed, adapted by self or externally instructed to change performance to adapt to the power supplied to the device. 
     In another alternative configuration, the pollution monitors of the oil facility  100  may typically report according to a predetermined sampling interval (e.g. every 15-minutes). However, this sampling interval can be increased or decreased based on various conditions. Examples of sampling interval changing conditions include, but are not limited to, temperature, solar energy levels, battery status level, presence of an environmental event, etc. For example, if the temperature has been low and the solar energy levels are low, the oil facility  100  can be preconfigured or instructed to increase the time between sampling intervals to preserve battery levels. Alternatively, if one or more of the individual pollution monitors of the oil facility  100  detect an environmental event, the interval reading time may be increased (e.g. to every minute). In other words, the sampling interval can be dynamically controlled according to a predetermined set of rules or updated as needed. 
     In another alternative configuration, the solar panel  140  ( FIG.  3   ) of the power system may be replaced by any of a variety of power supply/harvesting systems such as a thermo-voltaic power plant, a fuel cell, a large capacity battery, or grid-tied to the national grid via direct connection. These alternatives may or may not require the power management module  194  and/or the battery  198 . Additionally, the battery  198  may be single-use or rechargeable chemistry. 
     In another alternative configuration, the electronics package  150  may include at least one status indicator  218  that is visual or auditory. For example, the enrolling step during installation may include a flashing LED ( 218 ,  FIG.  8   ) on the electronics package  150  and/or a series of beeps that the installer can hear. These indicators (if provided) inform the installer about that status. 
     In another alternative configuration, the electronics package  150  may include a video recording module  220  for collecting, preserving and/or transmitting both stationery and video images of the monitored area  90 . 
     In another alternative configuration, the electronics package  150  may include a proximity, orientation, movement module  222 . If provided with this module/functionality, the location, orientation and any change in location can be collected, preserved and/or transmitted. 
     In another alternative configuration illustrated in  FIG.  32   , the individual pollution monitors ( 102 ,  104 ,  106 ,  108 ,  280 ,  282 ,  284 ,  286 ) can be configured according to a grid-pattern or as one or more concentric rings. The deployment and installation scheme is dictated by the type of monitoring to be accomplished and the topography of the oil facility  100 . 
     In another alternative configuration illustrated in  FIG.  33   , the amplitude of a leak event and the duration of a leak event may inform a determination. With reference again to  FIG.  33   , for example, the amplitude of hydrocarbon emissions from pollution monitor  106  as well as the duration of the time (e.g. 50 minutes) may reduce false positive leak events. For example, if a hatch on a holding tank is opened for pumping of oil, this might cause hydrocarbons to be emitted for 50 minutes. Therefore, watching the amplitude and duration of a leak event may inform that this is a typical event at an oil facility and not a ‘leak’ that requires repair. By manually, automatically, or through artificial intelligence monitoring various events will help to learn what are normal operating events to avoid false alerts. 
     In another alternative configuration, the housing  160  may further include tapered walls to enable the parts to be nested for easy distribution. Additionally, the corners of the housing  160  may include water drainage holes  165  for ejecting water that may happen to enter the interior portion. 
     In another alternative configuration, the electronics package  150  may be configured using off-the-shelf hardware such as open-source platforms (e.g. Arduino) to enable integrated wireless communications without extensive firmware development. By using an integrated wireless microprocessors and Arduino-based hardware, the pollution monitor  108  may be efficiently updated. 
     In another alternative configuration, the pollution monitor may be minimized to a simple wedge-shaped structure wherein the insulating body  110  is a simple wedge housing an interior portion. A bird passage may be provided to result in this interior portion being capable of housing a bird. Or, the insulating body  110  may be configured as a panel mount of any type of configuration. 
     In another alternative configuration, with reference to  FIG.  8   , the logic control system  190  and/or the watchdog system  192  may be configured to receive data from the communications module  204  to enable over the air (OTA) updating. While the OTA packet may include only one number or letter of change, it may (alternatively) replace every line of code for operating the pollution monitor or its larger system. These changes may be configured as needed depending on the intended outcome. OTA updates enable management of large numbers of remotely deployed pollution monitors and enables on the fly adjustments. 
     In another alternative configuration, methods for statistically removing ambient levels of emissions are utilized for processing large quantities of data and filtering that data to remove potential falsely-reported leaks and other emission events results in a clean data set. Studying background levels informs data science approaches to identify sensors which may have drifted out of calibration. This study enables patterns to reveal importance of human activity, weather events/cycles, time-of-day and other external factors. 
     In another alternative configuration, the pollution sensors are automatically compensated as best described with reference to  FIG.  6    wherein the pollution sensor  202  may ‘drift’ over time. If this change occurs, it may require baseline modification to adjust for the change (also referred to as ‘drift’). The pollution sensor  202  may be comparted to other sensors in nearby pollution monitors (e.g.  104 ) and calculations can be made either onboard (e.g. via the logic control system  190 ) or remotely (e.g. internet-attached web hosting server  420 ,  FIG.  32   ) to restore the functionality. 
     In another alternative configuration, pollution sensors that are designed for measuring one pollutant may have false-readings due to external conditions (e.g. metal oxide sensors may be sensitive to changes in humidity and temperature). While sensors may be programmed with onboard adjustment algorithms, the larger electronics package  150  may utilize other sensors (e.g. temperature, humidity, other sensors, etc.) to inform offsets that are due to environmental conditions verses those that are leak events. 
     In another alternative configuration, methods for aggregating bandwidth for cellular communications may be utilized as best described with reference to  FIG.  32    wherein one or more of the communications modules ( 204 ,  FIG.  15   ) may communicate with other nearby communication modules in other pollution monitors. This pollution monitor to pollution monitor communications may be referred to as peer-to-peer. In some instances, local communications may be all that is required as one of the pollution monitors may be ‘online’ (either fixed line or wirelessly). Alternatively, every third pollution monitor may include wireless communications to the internet-attached web hosting server  420  whereby one packet of data includes the readings from more than one pollution monitor. It should be apparent that by analyzing data consumption patterns of individual devices it may be possible to optimize the aggregation of data. In one illustrative embodiment, the various methods integrating wireless technologies to minimize bandwidth consumption, compression of specific data payloads, and adjustments to time of day and reporting frequency are all strategies to optimize the purchase of wireless bandwidth. 
     In another alternative configuration, database systems and architectures may be optimized for telemetry by utilizing non-conventional data storage techniques to optimize event storage. For example, rather than index in each row of data as it is stored (and possibly transmitted), indexing may be delayed until periods when telemetry streams are less congested. This reduces the bandwidth for transfer of traditional databases not designed for massive amounts of data. 
     In another alternative configuration, as best illustrated with reference to  FIG.  38   , another visualization tool may be provided to facilitate rapid dashboard implementation techniques beyond map modality and data modality. This expanded visualization tool may be employed to illustrate anomalies and the impact of a myriad of meteorological and environmental factors (that may include advanced statistical and visual representations). 
     In another alternative configuration, the pollution monitor and associated system(s) may be configured a business model where data is sold as a service. While some implementations of the described embodiment(s) may be simple cash-sales, others may be provided under a service agreement. Wherein the system is a service agreement, the service provider will handle the procurement of the pollution monitor(s) and/or deployment of the pollution monitor to the field. The recipient of the benefits and/or data will be invoiced and obligated to pay for the services. In one example, this will be a daily fee and, in another example, it will be an annual fee. The costs for this benefit may be born as a form of reparation for individuals or environment damaged by prior emissions, or the cost my be paid by municipalities. 
     In another alternative configuration, data science may be utilized to facilitate remote re-calibration of various components of a pollution monitor, or the larger system. Over time and with a large number of pollution monitors deployed, a large set of data will be developed. This dataset may be useful in reducing false-positives of leaks and/or remote calibration of sensors capable of adapting over time. 
     In another alternative configuration, the clean certificate may be created in-whole or in-part by an internal genesis block chain creation with a unique blockchain per pollution monitor. Each pollution monitor may uniquely derive a genesis block internally with its own microprocessor. Each pollution monitor may then produce its own blocks such that each canary will produce its own unique blockchain. The genesis block may be produced based on location (e.g. GPS data), hardware serial numbering (e.g. MAC address), base-line sensor data, and the other parameters. Furthermore, the blockchain hierarchy may be generated by each pollution monitor that may feed into different levels of blockchains. A first level may be a single pollution monitor blockchain. A second level may be a site (i.e. a first collection of pollution monitor), A second level may be a field (i.e. a second collection of pollution monitor that may include the first collection). A third level may be a basin (i.e. a third collection of  canaries  that may include the first and/or second collection. A fourth level may be a company. Each higher level blockchain may employ a smart contract or some other means to take as input blocks from lower level blockchains. For example, a company level blockchain may receive information from multiple basin blockchains associated with that company. Thus, the audit trail may follow several different blockchains. 
     In another alterative configuration, different levels of privatization of one or more components of a blockchain may be controlled through encryption. A company may want to keep data related to its pollution private until they clean up their act. Thus, a company may determine via encryption, access control lists, and the like, which parts of a blockchain are public. However, even if data is encrypted the trail of data may still be auditable. In one embodiment, a result of data within the blockchain may be made public, for example the measured PPM data may be encrypted but the resulting status of green, yellow, red may be made public, which identifies the current status of a particular site, basin, canary, and the like. 
     In another alternative configuration, certification of specific blockchain may be according to rules on what it takes to be certified may be public and stored in the blockchain. The rules may be based on geochemistry of each site. The certification specific blockchain may take as inputs sensor data from one or more sites and may rank those sites according to the public rules and output the rankings of those sites. The rankings may be dynamic in nature. The input into the certification specific blockchain may be a smart contract that only takes blockchain data from predetermined lower level blockchains. For example, data accepted by the certification specific blockchain may have to be from one or more registered sites. 
     In another alternative configuration, synch metrics may be modified whereby sampling frequency across pollution monitors may vary based on different events. For example, when a first pollution monitor detects a reading above pre-established noise-level then it may signal to neighboring pollution monitors to start sampling more frequently since it is likely a leak is happening. If pollution monitor are solar powered, they may reduce or increase frequency of sampling based on remaining power and/or weather forecast. 
     In another alternative configuration, an olfactory monitor may improve public relations and help to mitigate climate change through a process of creating a base-line reading and then monitoring for breach of the base-line reading. A pollution monitor may be provided with a pollution sensor (for example, a hydrocarbon sensor having a heat plate) to monitor and report foul-emissions that impact adjacent properties including a communications system for notifying a service company to deploy a repair crew. Pollution monitors may be utilized by home oil companies and homeowners alike (e.g. homeowners by oil facilities). The certification specific blockchain may take as an input canary produced blockchains at home locations to determine if there is an indecent within a particular neighborhood. This may be useful to determine “safe” neighborhoods and the like. Once it is determined that a particular site has breached a base-line (i.e. noise level) various actions may be taken by a canary within that site, such as initializing a microphone, taking one or more still pictures, sending alerts, open a summa canister (for sampling), and the like. These actions and the results of these actions may be saved in the blockchain for an audit trail. 
     In another alternative configuration, the pollution monitor and associated system(s) may be configured with a seismic event sensor (e.g. an accelerometer or other device utilized for indicating a seismic event). By accurately timing (e.g. via the GPS clock time) the arrival of a seismic event at each monitor, the location of the seismic event may be determined. 
     In another alternative configuration shown in  FIGS.  41  to  47   , an illustrative ornamental appearance of a pollution monitor may include an optional vertical object and other narrow aesthetic details. It is to be understood that features may be claimed as environmental features or simply removed to refine various embodiments of the present disclosure. 
     In another alternative configuration shown in  FIGS.  48  to  56   , an illustrative ornamental appearance of a pollution monitor may include optional (a narrow) aesthetic details. It is to be understood that features may be claimed as environmental features or simply removed to refine various embodiments of the present disclosure. 
     While the above description includes terms such as top, bottom, left, right, inside, outside, front, back, and other descriptors regarding physical orientation and/or position, it is to be understood that these are provided for illustrative purposes only. It is to be understood that the orientation of the pollution monitor  108  can be changed and the various descriptions may be confusing. However, the present description was provided to convey to one skilled in the art the embodiment(s). 
     While the principles of the disclosure have been described above in connection with the specific apparatuses and methods, it is to be understood that this description is made only by way of example and not as limitation on the scope of the disclosure.