Showing posts with label NH biomass. Show all posts
Showing posts with label NH biomass. Show all posts

Sunday, June 11, 2017

New Hampshire's Renewable Portfolio Standard – Part 4

My last three posts have looked into various aspects of NH’s Renewable Portfolio Standard (RPS). I presented the basic workings of the program,  discussed renewable energy credits (RECs) and REC prices and, most recently, looked at money flow and costs of the RPS program.  The program originally included a steady increase in the renewable energy (RE) requirement year on year; however, to reduce costs to electricity customers, some big adjustment in the requirements have been made over time to accommodate changing market conditions and the non-availability of RECs in specific classes. This post discusses the implications of some of those changes as NH gets back on track to meet its 2025 RPS goals. 

As noted previously, there are four classes of renewable energy in the NH RPS. Class I is for newer RE technologies, such as wind or ocean energy, and RE operations that have been commissioned since 2006. Class II is a special carve out for solar power. Classes III is for the older biomass operations, which include electricity generated from burning landfill methane or wood, and Class IV is for smaller hydro operations that were established prior to the end of 2005.

NH has an important forestry industry and eight wood-burning plants that generate electricity. Right from the start of the RPS program, a large Class III requirement  was put in place to support these wood-burning plants; however, from 2012 to 2016, the amount of RE from Class III was significantly curtailed to cope with the shortage of Class III RECs and to mitigate the cost of the shortage for ratepayers. The reason for the shortage was that the Connecticut (CT) REC market had high prices and had sucked in RECs from all over New England, including NH Class III RECs that qualified as CT Class I RECs. With limited NH Class III available, electricity suppliers would have been compelled to pay the Alternative Compliance Payment (ACP) instead, increasing costs to ratepayers.

In 2016 the NH Public Utilities Commission (PUC) held hearings on the topic and  were informed  that the REC market had changed, that CT REC prices had decreased, and there was testimony from the biomass coalition that sufficient Class III RECs would be generated and be available for purchase. Electricity suppliers weren’t convinced and, after deliberation, the PUC commissioners ruled to return the Class III requirement from 0.5 to 8% to put NH back on track to meet its RE ramp-up to meet the 2025 obligation, as shown in the chart below.


For 2017, the specific RE class requirements and associated ACPs are presently as follows:


Given this big ramp from 0.5% to 8%, I though it worth taking a closer look at the Class III REC market and the availability of biomass RECs to meet this requirement.

Let’s start with some basic calculations. Approximately 11,000,000 MWh of electricity are supplied annually to ratepayers and customers in NH. It follows that an 8% Class III requirement therefore needs to provide 880,000 MWh of electricity from pre-2006 biomass operations. The REC requirement is therefore also 880,000 MWh. That is a boatload of RECs – and the question is: Can that many RECs be generated from this source?

I then found the list of registered Class III providers at the NH PUC, which is provided below.


Closer examination of this list brings to light the following:

  • There are 20 registered Class III operations, providing a total generating capacity of 137 MW. Most of the operations (13 of 20) are from out of state.
  • Only three of NH’s eight wood-burning plants (highlighted in green) are registered as Class III producers: the rest, such as the large Berlin biomass operation, appear to be registered as Class I producers.
  • Of the 137 MW of Class III capacity available, the NH wood-burning plants only provide 56 MW, or 41% of the total capacity: the rest comes from in-state and out-of-state landfill methane operations.
  • If we include the NH landfill methane operations (highlighted in grey) with the NH-based wood plants, only 68 MW, or 49% of the total capacity, is provided by NH-based plants: the rest is from out-of-state landfill gas operations in RI, NY, and VT.
I found all of this surprising because my understanding is that the original intent of including the Class III category in the NH RPS was to support NH biomass operations.  Instead, in its present form, it seems to be doing a lot to support out-of-state landfill operations.

Let’s return briefly to some calculations. If we take that 137 MW of Class III generating capacity and assume that the generating plants are operational for 90% of the time (see my I’ve Got the Power post for a discussion of capacity factor and the difference between generation capacity and energy), we can determine how much electricity should be generated over one year: 137 MW x 0.9 x 365 days x 24 hours/day. This calculation gives 1,080,108 MWh or RECs. This is a useful result because it suggests that there could be production of sufficient RECs to cover the 880,000 that we need. In fact, the calculation suggests that we might potentially have an excess of Class III RECs, which hopefully will drive their prices down and save money for NH ratepayers.

REC producers in New England are required to register and file their REC production data with the New England Power Pool Information System (NEEPOL GIS). Some of the data is available to the public. I noted that in 2015 and 2016, 1,005,258 and 924,716 NH Class III eligible RECs were produced, respectively. This is right in line with my calculation of 1,080,108 RECs. Historically, there seem to be sufficient Class III RECs to meet NH’s needs.

However, availability does not obligate producers to sell into the NH REC market. They could, especially if prices are high, elect to sell, as in previous years, into other markets, such as the CT Class I market. If insufficient Class III RECs are available, prices will quickly rise close to the Class III ACP cap of $ 45. As a biomass RE generator, that is what I would want and I might choose to direct some of my RECs to a different market to support higher NH Class III REC prices. This is a direct consequence of our inconsistent and changing REC market in New England. It provides opportunities for good traders to play off the differences between markets—and it makes perfect business sense to do so.  

However— and this is a big HOWEVER— the calculation of a surplus assumes that all operations run 90% of the time, that there are no major shut downs at any of the larger facilities, and that biomass REC producers don’t elect to sell Class III in other eligible markets. Another complicating factor is that there is legislation, known as SB129 presently making its way through the NH General Court that makes important modifications to the RPS program, especially in the Class III category. Just last week, the NH House approved a change in the RPS law that promotes NH biomass in two ways:

  • It would put a 10 MW limit on the size of landfill methane operations that qualify for Class III RECs. This change appears to be directed at eliminating some of the large out-of-state landfill operations from RI and NY that have been participating in the NH Class III market.
  • The ACP for Class III RECs would be increased to $ 55, which should increase the REC prices in the case of a Class III REC shortfall.
If we go back to the list of Class III operations above, I have highlighted two potential operations that may not qualify for the production of Class III RECs under the new 10 MW limit: the first is the large Johnston landfill in RI, highlighted in orange, and the second, highlighted in blue, is the Seneca landfill in NY (if its combined output is considered).  If both of these landfills are excluded, this would lead to a 36.3 MW reduction in Class III REC generation capacity, which represents an overall decrease of 26%. This would result the production of only 794,000 RECs, which is short of the 880,000 that NH needs in Class III. What are the consequences of this shortfall?  This means that the prices for Class III will climb to close to the value of the price cap (the ACP) and the shortfall will be made up by utilities having to pay the ACP. 

The next question is: What are the implications of these changes to NH ratepayers? Let’s turn again to some calculations and assume that those 794,000 RECs sell for 90% of the $ 55 ACP, or $ 50, and that the shortfall of 86,000 is paid in as the $ 55 ACP. In this case, we can calculate that the Class III requirement of 8% and the higher ACP could cost NH electricity customers some $ 44 million annually. If we apply this amount over the 11 billion kWh of electricity sold annually in NH, the rates can be expected to increase by 0.4 cents/kWh. For a NH residential customer using 600 kWh per month, this could result in an annual electricity cost increase of about $ 30. 

I did extend this calculation to determine a total cost for the RPS program for 2017 based on lower Class I REC prices and some significant assumptions on REC availability and prices in the other classes. My calculations led to an RPS cost of approximately $77 million which is 4.7% of the $1.7 billion I’m assuming will be paid for electricity by NH ratepayers in 2017 (based on $150/MWh ($0.15/kWh) retail rate and 11 million MWh of electricity). This is a significant increase over the 2.6% value I calculated for the 2015 RPS program in my previous post.

Now, bear in mind that these are rough back-of-the-envelope calculations; they do, however, give a sense of the potential implications for NH ratepayers of the Class III ramp up to 8% combined with the proposed RPS SB129 legislation. Perhaps I am dead wrong in my assumptions. Maybe the Class III generators will produce RECs beyond their rated capacity, perhaps not all of those highlighted out-of-state landfills will be excluded from the Class III list, and perhaps the Class III generators will choose not to sell any of their RECs into the CT Class I market. In this case, a surplus of Class III RECs will be produced, prices will be much lower, and the costs to NH ratepayer will be reduced. There is even the possibility that the PUC could jump in again to ratchet down that Class III requirement, as they have in previous years. Regardless, this is certainly food for thought as the SB129 legislation makes its way through the lawmaking machine and onto the Governor’s desk.

This is a complicated matter and it presents a huge dilemma for legislators, regulators, and the wood-burning plants in NH. On one hand, as pointed out in my post, Between a Rock and Hard Place, the NH wood-burning plants absolutely need the REC revenue and higher REC prices to survive. In fact, one such plant, the Indeck Energy plant in Alexandra, recently closed down  due to low wholesale electricity and REC prices. Alternative forms of electricity generation are also very important and wood-burning capacity helps to reduce our dependence on natural gas-fired generation. But, on the other hand, legislators and the PUC commissioners need to weigh the cost of the REC-based subsidies of the biomass industry against costs to ratepayers. There are no easy answers and these are difficult decisions to make.

Feel free to weigh in on this issue because it is a surprisingly important one. In the meantime, do your part to reduce our need for electricity from any generation source by remembering to turn off the lights when you leave the room.

Mike Mooiman
Franklin Pierce University
mooimanm@franklinpierce.edu


Monday, April 8, 2013

Songs from the Wood* - Wood Fired Electricity in New Hampshire – Part 1

In my last post we took a look at energy sources and costs for home heating, and we saw how relatively inexpensive wood is compared to most other fuel sources in New Hampshire at the moment. Only natural gas is cheaper on a dollar per heat content basis. Wood as a fuel is particularly intriguing in the New Hampshire context. A great deal of NH is forested. In fact, 84% of the State is forested and, of the 5.7 million acres of land in New Hampshire, 81% is viable timberland. Therefore, tree harvesting for electricity or home heating applications is a way we can use a local in-state resource to reduce imports of fossil fuels like coal, oil or natural gas. Utilization of NH forests also provides a lot of local jobs and, over the 20 to 30 year life of a tree, wood combustion does have a lower carbon footprint when compared to fossil fuels. 

Many folks believe that, over the long term, the use of wood for energy purposes can be viewed as being carbon neutral. In other words, the carbon dioxide that is released in the combustion of wood is offset by the carbon that was absorbed by the tree during the process of photosynthesis which converted the carbon dioxide into the organic matrix of the tree. This is not entirely correct as there is not a one-to-one correspondence of carbon dioxide in = carbon dioxide out. We have to take into account that a great deal of fossil fuel energy is used to manage the forest, harvest the wood, transport it and convert it into a form, such as firewood, woodchips or wood pellets, which can then be combusted. As a result, the total amount of carbon emitted in utilizing wood as a fuel source is greater than that absorbed during photosynthesis.
 
We generate a good amount of electricity in New Hampshire from the combustion of wood. In 2011 we produced 1.03 million megawatt hours (MWh) of electricity from wood-fired operations, which is equivalent to 5.1% of the total electricity produced in the State. There are presently seven wood-burning plants that generate electricity from wood chips in New Hampshire and this year we should see the commissioning of the State's largest wood-fired power plant, the Burgess Biopower plant, which is located in Berlin on the site of the old Frasier Paper Mill. This new power plant will increase the overall percentage of electricity generated from wood from 5.1 to 7.5%.
 
The map below shows the location of the various wood-fired electricity plants in NH and the table that follows provides the key for the locations shown on the map as well as information about the various operations.




The data in the table show that most of the wood-fired power plants are smaller operations with capacities of the order of 15 to 20 MW. At this time, the largest operating plant in the state is the 50 MW Northern Wood Power plant. This facility is owned by our largest utility company, Public Service of New Hampshire, PSNH, and is located in Portsmouth on the Schiller power plant site. This plant was started up in 2006, when PSNH converted one of the three large boilers at the Schiller station from coal to a wood chip fuel source. Most of the other wood-fired operations were built in the late 1980s when New Hampshire was encouraging home grown energy and PSNH was required to sign 20-year power purchase agreements with these new wood-fired operations. Over time, there has been a fair amount of change in the ownership of some of these plants as the attractions and economics of renewable energy have waxed and waned.
 
The generation of electricity from wood is an intriguing business and one that is full of opportunities and challenges – some of which I will discuss my next post. In the figure below I have sketched the value chain for the wood-fired electricity business, along with some of the important inputs and outputs.

 
In the first step, we have the lengthy process of tree growing and the incorporation of carbon into the organic matrix of the tree and sunlight into stored chemical energy – both of which will eventually be released during combustion. Active and scientific forest management is required to allow trees to grow to their full potential. This has to be done while countering insect infestations, drought, fire and a host of other problems. The average life of a tree is typically 20 years before it is harvested.
 
In step 2, we have the harvesting of trees from public and private lands. This process is now highly mechanized and involves large machines to take down the trees, remove the brush and load them for transportation. Because it is highly mechanized, a lot of fossil fuel, in the form of diesel and gasoline, is used, so there is a net energy input into this step.
 
In step 3, the logs are transported to the saw mills where they are converted into lumber, wood chips for paper pulp, wood chips for combustion and waste sawdust. A great deal of the waste sawdust is converted into wood pellets which many folks use as fuel in their wood-fired home furnaces. The sawmill conversion process is also highly mechanized and automated, and it too requires a large energy input. I will note that it is possible to combine the harvesting and chipping operations right on site where the trees are harvested. In these operations, the trees are taken down and are immediately run through a large wood chipper. The wood chips are then directly loaded onto trucks for transportation to the wood-fired power plants, thus bypassing the saw mills.
 
Finally in step 4, wood chips from the saw mills or chipping operations are then transported to the wood-burning plant, where they are stored in enormous storage piles. The wood chips then become the fuel for the power plant, and they are burned in large furnaces where the heat is used to boil water. The steam is then used to drive a turbine which drives an electrical generator that produces electricity. Other than wood chips, there are inputs of water and skilled labor as well as fossil fuels used to transport the wood chips into the feeders.
 
These wood-burning operations produce electricity that is fed into the electrical grid but an enormous amount of waste heat is produced as well. In a previous post, I provided data that showed that only a small fraction, 23%, of the chemical energy in wood is converted into electricity. In contrast, coal-fired power plants have conversion efficiencies of 31% and natural gas plants, on average, have efficiencies of 45%. The 77% of waste heat from these wood-fired operations is dissipated by the evaporation of water and by the hot gases exiting the tall emissions stacks from these operations.
 
A fact that is not often appreciated is that a lot of water is utilized in the production of electricity. The water is used to produce steam and to cool the off-gases and, as such, a lot of water is lost to the atmosphere via evaporation. It has been estimated that water consumption for electricity generation is of the order of 4000 to 8000 gallons per MWh of electricity produced. One megawatt hour represents the approximate monthly electricity consumption for a US home so every month your electricity usage results in the consumption of 4000 to 8000 gallons of water. However, it should be noted that the water consumption numbers for wood-fired power plants are substantially lower. Saving on water consumption is just another reason to turn off the lights and save electricity. A point I often make to students in the Franklin Pierce University MBA in Energy and Sustainability Studies program is that if you are in the energy business, you are in the water business as well.
 
A small amount of wood ash is produced from these operations and this is a valuable soil additive that is used by local farmers.
 
So if we step back and look at the energy and carbon dioxide flow aspects of the wood-fired electricity business, it is clear that it is a lengthy and involved pipeline from photosynthesis to electricity. It takes time, money, energy, labor, and fossil fuels to get forests to incorporate sunlight and carbon dioxide into the body of tree and for us to release that energy (and carbon dioxide). As a result of all the various fossil fuel-based energy inputs all along the way, it is clear that wood burning cannot be viewed as entirely carbon neutral. However for us, here in forested NH, wood does represent a better fuel source than imported fossil fuels which have no offsetting carbon absorption and the wood-fired electricity does provide a lot of jobs and livelihoods as we move along the chain from photosynthesis to electricity. Now if we could only do something about that 77% of wasted energy…..
 
In my next post I will take a brief look at the economics of producing electricity from wood, and I will wrestle with the issue of just how much wood could we burn in New Hampshire before we overtax our forests. In the meantime, remember that it takes a lot of fossil fuel, labor and water to convert the chemical energy in wood into electricity we use in our homes. Many times the songs we play in our homes on our CD players are powered by our forests. These, indeed, might be Songs from the Wood.
 
Until next time, remember to turn off the lights when you leave the room. You will be saving energy and water.

Mike Mooiman
Franklin Pierce University

mooimanm@franklinpierce.edu
4/8/13

 
(*Songs from the Wood was the title of and a song from Jethro Tull's tenth album. This album, with its distinct British folk rock sound, was quite a departure from Tull's earlier heavy rock and blues influenced recordings. This recording cemented Jethro Tull's reputation as a bunch of odd ducks making interesting and influential music. The cover art on the album also features the results of some wood harvesting. An old tune but worth a listen).