Carver L, Sullivan S
Birkbeck College, Malet Street, London, WC1E 7HX, U.K.
Bath Spa University, Newton Park, Newton St, Loe, Bath BA2 9BN, U.K.
Conserv Biol. 2017 Oct;31(5):1053-1065. doi: 10.1111/cobi.12917.
We examined and analyzed methods used to create numerical equivalence between sites affected by development and proposed conservation offset sites. Application of biodiversity offsetting metrics in development impact and mitigation assessments is thought to standardize biodiversity conservation outcomes, sometimes termed yield by those conducting these calculations. The youth of biodiversity offsetting in application, however, means little is known about how biodiversity valuations and offset contracts between development and offset sites are agreed on in practice or about long-term conservation outcomes. We examined how sites were made commensurable and how biodiversity gains or yields were calculated and negotiated for a specific offset contract in a government-led pilot study of biodiversity offsets in England. Over 24 months, we conducted participant observations of various stages in the negotiation of offset contracts through repeated visits to 3 (anonymized) biodiversity offset contract sites. We conducted 50 semistructured interviews of stakeholders in regional and local government, the private sector, and civil society. We used a qualitative data analysis software program (DEDOOSE) to textually analyze interview transcriptions. We also compared successive iterations of biodiversity-offsetting calculation spreadsheets and planning documents. A particular focus was the different iterations of a specific biodiversity impact assessment in which the biodiversity offsetting metric developed by the U.K.'s Department for Environment, Food and Rural Affairs was used. We highlight 3 main findings. First, biodiversity offsetting metrics were amended in creative ways as users adapted inputs to metric calculations to balance and negotiate conflicting requirements. Second, the practice of making different habitats equivalent to each other through the application of biodiversity offsetting metrics resulted in commensuration outcomes that may not provide projected conservation gains. Third, the pressure of creating value for money diminished projected conservation yields.
我们研究并分析了用于在受开发影响的场地与提议的保护补偿场地之间建立数值等效性的方法。生物多样性补偿指标在开发影响和缓解评估中的应用被认为能够使生物多样性保护成果标准化,进行这些计算的人有时将其称为产出。然而,生物多样性补偿在实际应用中尚不成熟,这意味着对于生物多样性估值以及开发场地与补偿场地之间的补偿合同在实践中是如何达成的,或者对于长期保护成果,人们了解甚少。在英国政府主导的一项生物多样性补偿试点研究中,我们研究了场地是如何变得可比的,以及如何针对一份特定的补偿合同计算和协商生物多样性增益或产出。在24个月的时间里,我们通过多次走访3个(匿名的)生物多样性补偿合同场地,对补偿合同谈判的各个阶段进行了参与式观察。我们对区域和地方政府、私营部门以及民间社会的利益相关者进行了50次半结构化访谈。我们使用定性数据分析软件程序(DEDOOSE)对访谈记录进行文本分析。我们还比较了生物多样性补偿计算电子表格和规划文件的连续版本。特别关注的是一项特定生物多样性影响评估的不同版本,其中使用了英国环境、食品和农村事务部制定的生物多样性补偿指标。我们突出了3个主要发现。第一,随着用户调整指标计算的输入以平衡和协商相互冲突的要求,生物多样性补偿指标以创造性的方式得到了修正。第二,通过应用生物多样性补偿指标使不同栖息地相互等效的做法导致了等效结果,而这些结果可能无法提供预期的保护增益。第三,创造性价比的压力降低了预期的保护产出。