Reducing Forest Residue Volume

One drawback of current forest restoration treatments is that slash is often burned in piles that may damage the soil and require further restoration activities. We look at several alternative methods for reducing forest residues while minimising detrimental impacts. By Deborah S Page-Dumroese, USDA Forest Service

 

 

Many forest stands in the western US are in need of restoration for a variety of attributes (such as fire regimes or watershed health) after 100 years of fire suppression, selective harvesting, or livestock grazing. 

 

Although there is broad agreement that some form of restoration of fire regimes, habitat, fish, and wildlife populations, or disturbance patterns is necessary in many areas of the western US, there is disagreement about the objectives and implementation strategies. 

 

Stand density restoration activities usually involve cutting and removing small trees with little merchantable value. Residues created from thinning activities designed to reduce wildfire were estimated to be approximately 0.2 million metric tonnes annually in the forests of Southern California and were expected to increase to 1,500 metric tonnes per day. 

 

To reduce the risk of wildfire, residues are often removed and transported to a bioenergy facility, dispersed across the harvest site by masticating or grinding them, or piled and burned.

 

 

Slash pile burning can be an economical method for disposing of harvest residues on National Forests following timber harvesting operations and an effective method for reducing the volume of unmerchantable material. However, the impact of pile burning on soil processes is highly variable and can result in either relatively small impacts for a short period of time or long-term residual soil damage, but the ecological impacts are not well understood. 

 

The high variability of soil impacts from pile burning impacts can be attributed to differences in soil texture, fuel type and loading, soil moisture, and weather conditions during burning. Often, slash piles leave only localized soil impacts; however depending on postharvest woody residue abundance, pile size, amount, and type of fuel in the piles, soil type, fire duration, and the distribution of piles within an activity area larger-scale impacts are possible. 

 

Alternatives to slash pile burning are limited and broadcast burning is often restricted by weather conditions, stand species composition, availability of expert fire crews, or air quality regulation that limit seasonal burning. Some areas are not suited for pile or broadcast burning and therefore, mastication (reducing the size of woody residues) is gaining popularity in many areas because it can be less expensive than burning. However, it does not remove fuels, it just rearranges them.

 

Slash Pile Impacts

Determining the impacts of pile burning on soil health is complex because of the wide variability in how piles are constructed and distributed within a harvest area, amount of biomass to dispose, piling method, species composition, and pile location. 

 

In addition, soil is not a particularly good conductor of heat owing to its high internal porosity. For example, hand-built pile coverage in a Lake Tahoe Basin study ranged from two percent to over 30 percent within thinning units. 

 

In northeastern Oregon, estimates for whole tree yarding and bulldozer-built piles are one on four ha (10 acres) while processing trees within a harvest area may result in one bulldozer-built or hand-built pile in every 0.4 ha. 

 

Commonly, harvest units have less than 15 percent pile coverage (median of 8 percent) and the actual ground coverages are highly correlated with the level of basal area reduction.

 

Because slash is concentrated into piles, heat is concentrated into a small area where it can alter soil structure, infiltration, nutrient cycling, soil pH, and microbial populations. 

 

Pile burning can also impact understory plants, seedbanks, and water holding properties. Many studies suggest that pile burning occur when soils are moist to limit detrimental soil heating, despite the potential for biological damage that can result from burning piles when the soil is moist.

 

When slash piles are built using a bulldozer they are often a mixture of dense fuels, mineral soil, and surface organic horizons. Once ignited, the piles often burn very hot for an extended period of time and can produce long-term soil impacts. 

 

Pile size also plays a key role in soil impacts. Season of burning and under-pile soil moisture and texture will alter the extent of impacts. In northwestern Montana, for example, spring burning of grappler-built slash piles on fine-textured soil resulted in increases in soil organic matter, carbon, and nitrogen. 

 

Fall burning of grappler-built piles when soil moisture was low resulted in loss of more than half of the organic matter, carbon, and nitrogen. There are methods to restore burn scars (such as wood chip mulches or soil scarification), but these efforts also add to overall increased site preparation costs.

 

Biochar Making

There has been increased interest in using woody residues generated from thinning or bioenergy harvests to make biochar. However, transportation costs to move unmerchantable woody material to a pyrolysis unit can be expensive, as can the pyrolysis equipment itself. 

 

Therefore, creating biochar on-site can be less expensive and immediately applied back on a site as a soil amendment or to restore skid trails, log landings, or burned areas.

 

Traditional slash pile burning can result in some recalcitrant carbon (black carbon, biochar) produced under the burn area, but the amounts remaining depend on burn temperature, with black carbon originating at temperatures between 250 and 500 deg C. 

 

Biochar is about 80 percent carbon and less than 0.1 percent nitrogen, and its porous nature makes it potentially beneficial for increasing water holding capacity and decreasing bulk density. It also alters cation exchange capacity and soil colour and is the location of many ectomycorrhizal fungi. 

 

Biocharcan be used to restore soil function in areas where there is a loss of organic matter. One other potential use of forest residue-produced biochar is to augment lost soil organic matter in dryland farming. 

 

Charcoal forms naturally at a rate of 1–10 percent during wildfires. On some sites, charcoal has been found dating back 11,000 years before present, but the quality of charcoal and its’ recalcitrance is dependent on climate, soils, and plant species. 

 

Current efforts to convert biomass that would normally be burned in slash piles to biochar can result in 10–35 percent by volume inputs of carbon into the soil. This carbon is more stable and has a lower risk of releasing carbon dioxide or other greenhouse gases into the atmosphere. 

 

Amending sites with biochar during farming production or on forest sites after harvesting further protects biochar from degradation as it becomes part of the stable carbon pool.

 

Alternative Methods

To maximize the creation of charcoal the burn pile was elevated above the soil surface on large logs, with smaller material piled perpendicularly on top. 

 

Grapplers were then used to build a pile on the base logs. There are several advantages to elevated piles: (1) potential for greater air flow to dry woody material, (2) limited moisture wicking up from the soil into the wood, (3) construction time is similar to other only pile-building methods, and (4) potential to limited soil impacts to the areas where the base logs are in contact with the soil. 

 

Base logs for this type of slash pile can be as small as 10 cm in diameter and still provide protection to the soil.

 

Production of biochar from this type of pile can be raked into the soil around the burn area for restoration of compacted soils or to provide additional organic matter near the pile. 

 

Kilns

Kilns have been used for centuries to make charcoal. Often built as earth-covered pits or mounds, traditional kilns provided an inexpensive, efficient means for charcoal making. Other kilns have been made of brick, metal, or concrete. 

 

Kilns operate in batch mode in which feedstock is added and charcoal is removed. However, newer kilns can provide automatic feed.

 

Metal Kiln

Kilns made of metal were designed to be relatively portable. They have two cylindrical sections and a conical cover with four steam release ports and the bottom section sits on four inlet ports. 

 

Air flow into and smoke out of kiln can be controlled through the ports so that both charcoal quantity and quality can be controlled. During production, wood biomass is reduced by approximately 65 percent. 

 

One batch takes approximately two days to complete which includes loading the kiln, lighting the fire, adding the chimneys, and closing off the inlet ports. 

 

Multiple kilns at one site can process the residues more efficiently. Because the kiln is constructed in section, it can be loaded onto a trailer for transport to the harvest site. 

 

Metal kilns can be used in remote areas accessible by a pickup truck and the feedstock needs little postharvest processing, such as chipping. In addition, unskilled personnel can be quickly trained to operate the kiln. 

 

Charcoal produced from this kiln has approximately the same dimensions as the wood that was put into it. However, the charcoal fragments easily and driving over it with a large truck shatters the charcoal to make it easier to spread. 

 

Rotary Kiln

Rotary kilns were developed for large-scale forest harvest operations which generate large volumes of woody residue. A rotating metal tube is heated from the outside with gas burners to temperatures of 400 to 600deg C. 

 

The tube is in constant motion which quickly exposes woody residues to extreme temperatures, allowing the feedstock (wood chips) to be rapidly heated. The extreme heating of small particles in a low oxygen environment quickly transforms the wood into three potentially high-value products biochar, biooil, and syngas. At times, biochar is the targeted output, but for other applicationsbiooil may be the desired output.

 

The entire rotary kiln unit is housed in a shipping container or trailer making it relatively portable into a forest environment. It also requires a trailer to move supporting equipment that includes hoppers and feed bins, a high-lift forklift, and an electrical generator.

 

Rotary kilns can process up to 20 tonnes of feedstock in 24 hrs. The ideal chip size is 1.3 cm or less, to maximise throughput. It is also ideal to have the feedstock as dry as possible, less than 10 percent moisture. 

 

The machine will function when the feedstock is very wet and wood particle size is up to 5 cm, with the throughput and char quality significantly reduced and an increased risk that a large wood piece will damage the equipment. 

 

The dimensions of the feedstock remain unchanged through the pyrolysis process biochar looks similar to the chips except they turn black after processing. When focused on biochar production for agriculture it is most desirable to have small, consistently sized feedstock so the material will mix well with soil or be deployed using a lime spreader or other agricultural spreader-type equipment. In forest operations, the biochar does not have to be uniform and can easily be spread on slopes, log landings, or skid trails using the biochar spreader.

 

In addition to being relatively mobile, another advantage of the rotary kiln is the control it offers the operator. Adjusting the temperature and the time the wood chips are in the kiln will produce biochars of different qualities. 

 

Biochar can be more effective if its chemistry is designed to target specific soil quality issues. For example, in locations where crop yield increases are not a goal, biocharcan be used to sequester carbon. However, improving water holding capacity, infiltration, or nutrient retention may be achieved by biochar designed for these purposes. 

 

Biochar made in kilns tend to have higher carbon and nitrogen contents than biochar from slash piles or the air curtain burner.

 

Mini Kiln

These simple, low cost kilns are operated primarily by family forest owners (generally < 500 acres) interested in conservation stewardship of their land. 

 

The appeal comes from recognizing the benefits of biochar as a soil amendment and as a mechanism to sequester carbon from the atmosphere, along with a desire to seek alternative means of managing thinning residues besides pile burning. 

 

A main attribute of the mini kiln is its light-weight construction for easy transport by 1-2 people. Design characteristics of the kiln (shape, volume, and thickness of metal walls) are user defined, often by a trial-and-error process. 

 

The advantages of mini kilns are their low cost, ease of use, and transportability. Because of the relatively small scale of this operation, the quantity of biochar produced is generally limited, and the products are often used for improving soil tilth of nearby gardens, small orchards, or pastures. 

 

Again, this operation is geared to meet the needs of small-land owners; efforts to scale-up the use of mini kilns to treat thinning residues on a stand-level basis are of growing interest and will likely hinge on the economic feasible of biochar production relative to pile burning.

 

Forest Management Implications

Currently, forest restoration or rehabilitation treatments involve forest thinning and regeneration harvests that can produce 40–60 million dry metric tonnes of woody biomass per year. 

 

Forest thinning operations, coupled with creating and spreading biochar, benefit both soil and forest health. Unlike agricultural soils where biocharcan be added and tilled into the soil profile, application of biochar on forest sites is more difficult since trees, stumps, and downed wood hinder equipment movement across a site. 

 

However, in managed forests log landings, skid trails, abandoned roads, or abandoned mine land soils all require some form of restoration. Using a biochar spreader on these types of soil and sites is an ideal way to spread locally created biochar.

 

Given the large volumes of woody biomass created during harvesting in many forests, excess biomass may be converted to biochar and used by agricultural producers. This biochar creates a new market for timber purchasers to consider when bidding on harvest units. In addition, with the more wide-spread use of kilns and other methods to create biochar, areas with dead or unmerchantable timber from drought, disease, insect, or wildfire may be a feedstock source for biochar production and help lessen the future risk of wildfire.

 

Many North American forests face management challenges related to wildfire, insect and disease outbreaks, and invasive species resulting from overstocked or stressed stands. These forest stresses are already being exacerbated by climate change and therefore, creating and amending soil with biochar may be one method to mitigate soil drought conditions and sequester carbon

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