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We found that provincial-level times replacing advantages of future fuels was in fact somewhat smaller compared to those projected out of latest fuels (Fig

We found that provincial-level times replacing advantages of future fuels was in fact somewhat smaller compared to those projected out of latest fuels (Fig

I thought low and you will highest substitution pros regarding the analyses once the suspicion regarding the replacement experts leads to uncertainty in mitigation overall performance to own times and you will items . 4), but contemporary fuels got deeper regional distinction, especially for nations with a high industrial opportunity demand and lower populace, just like the conclusions out-of an earlier study . For future analyses, it might be advantageous to has actually spatial details about upcoming society and you can industrial fuel useage for each fossil fuel.

In remote organizations, energy fool around with is changing as a consequence of numerous software (the Clean Opportunity for Rural and you can Secluded Communities (CERRC) program , this new Indigenous Out of-Diesel Effort , and also in 2018 the fresh CleanBC package revealed the mark to minimize of the 2030 brand new diesel usage in off-grid communities of the 80%

Uncertainty on replacing experts to own intellectual chat room wood activities is actually reviewed by using large and you can lowest replacing masters to have sawnwood and boards. A recently available review of education that have analyzed replacing experts having timber , found an average unit displacement factor that is within the variety regarding thinking utilized in this study, however, additional information on displacement things by product type of and you will country could well be useful, in addition to additional information on prevent-spends and related product lifetimes (elizabeth.grams. [5, 8]). Information regarding replacing masters to have pulp and you may paper is bound, therefore presumed there is zero replacing work for, but considering the proportion regarding C inside class (25% to help you 34% out-of wood products), polishing these types of affairs might have highest impacts on the net GHG reduction. Long lasting uncertainties towards genuine magnitude away from replacement positives, the results demonstrably show that better mitigation pros is possible as a result of regulations that (1) help the C storage time in gathered wood situations of the favouring long-existed more brief-stayed activities also bioenergy, and you may (2) encourage the entry to timber points to change emission-intensive product, elizabeth.g. regarding the strengthening field.

not, no change in markets costs off HWP was assumed in virtually any scenario because the HWP costs are usually dependent on highest-level locations if you are diary segments was apparently local

In terms of the economic analyses, similar studies have compared mitigation costs for various mitigation scenarios at the national scale and for specific activities [45, 56, 68]. In this study, we used regionally differentiated economic assumptions by three broad regions (northern interior, southern interior, coastal region) as well as at the timber supply area (TSA) level for the Bioenergy scenarios in order to capture the spatial variation in market price and production cost (Additional file 1: Table S9). The cost and price assumptions associated with the bioenergy scenarios and the substitution effects were TSA-specific depending on residue availability, bioenergy facility type, transportation distance (simple estimates), and fuel mix. We assumed that log prices would be affected if harvest shifted among log grades due to mitigation scenarios. For example, the Higher Recovery scenario was assumed to increase the proportion of logs in lower grades and thus reduce overall average log prices, while the Restricted Harvest scenario was assumed to decrease the portion of top-grade logs, and therefore also reduce overall average log prices. Costs related to forest management were affected if harvest activities were altered by mitigation scenarios, for instance, logging costs increased in conservation scenarios because more dispersed cut blocks were needed to keep the same harvest characteristics (e.g., diameters, tree species, etc.). We also assumed a fixed $50/tCO2e carbon price over the entire period for slashburning as a penalty in the baseline to reflect a possible policy change to include slashburning in BC’s existing carbon pricing . Manufacturing costs were also impacted by changes in production efficiency that then depend on the availability of input materials. Additional recovered fiber under Higher Utilization was assumed to be used in HWP following the same proportions as in the baseline, thus a lower manufacturing cost was assumed for pulp and paper production due to higher efficiency, but a higher manufacturing cost for solid wood products because of lower log quality. Similarly, higher manufacturing costs were assumed for all HWP in the conservation scenarios due to lower efficiency. In the LLP scenario, we assumed economy of scales increased manufacturing costs of pulp and paper (+ 2%) and decreased costs for solid wood products (? 2%) .

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