Low input parks strategy can work: Dynamic profile of Mishmi Takins under constrained conservation management in Mt. Gaoligong, China

A landscape persistence-based methodological framework for assessing ecological stability

Ecological stability is a critical factor in global sustainable development, yet its significance has been overlooked. Here we introduce a landscape-oriented framework to evaluate ecological stability in the Qingzang Plateau (QP). Our findings reveal a medium-high stability level in the QP, with minimal changes over recent years. The driving factors vary across landscape types, with climate and anthropogenic factors emerging as crucial determinants. While anthropogenic factors are strong but unstable due to policy changes and economic development, climatic factors exert a consistent influence. Based on our results, we propose site-specific ecological conservation and restoration measures. The ecological stability assessment framework provides a practical tool to understand the link between environmental conditions and ecosystems.

Administrative Level May Be the Key Factor to Improve Protection Effectiveness of Nature Reserves in China

Nature reserves (NRs) have been the backbone of biodiversity conservation and the construction of China’s ‘ecological-civilization’ since the 1950s. With over 11,800 protected areas (PAs) covering 18% of the country’s land area, Chinese NRs have made a great contribution to global biodiversity conservation. At this point, better protection effectiveness can be achieved by optimizing the management organization rather than expanding the area. We analyzed the management structure of Chinese NRs by looking at their ranks, the hierarchy of administrative organs, number of grass-root stations, manpower, and financial resources, among other variables. We found that the average number of staff employed and yearly financial input per km2 of Chinese NRs were both higher than the world and US averages. However, the range was extremely high, revealing great unbalance among different regions and ranks of NRs. In particular, the western part of China, which is less developed and features the least disturbed ecosystems, received less funding and staff resources than the developed east. A further analysis of the highest-ranked nature reserves, i.e., the national nature reserves (NNRs), showed that administrative organs of different hierarchical statuses (the lowest being Deputy family, the highest being Division level) could be in charge of them. Unexpectedly, we found that the amount of human and financial resources injected into NNRs was correlated with the level of their administration but dissociated from other important factors such as the reserve’s size or ecological value. Furthermore, the management organization was inadequate, with many NRs lacking key departments as defined by Chinese nature reserve regulations. We suggest that the administrative levels of management organization in NRs should be unified, and through the existing ecological transfer payments policy, strengthen the financial and staffing input in the western NRs of China. Moreover, the internal structure of NRs management should include all relevant departments with specific tasks and the creation of grass-root stations should be promoted without neglecting the capacity building to improve staff’s knowledge.

The effective use of camera traps to document the northernmost distribution of the western black crested gibbon in China

Gibbons represent a highly successful radiation of four genera and 20 species of Asian apes that, in response to recent habitat fragmentation and deforestation, are threatened with extinction. China has six species of gibbons, each of which is critically endangered. We present new biogeographical information on the distribution of the black crested gibbon (Nomascus concolor). Four subspecies of N. concolor have been described: three of them are present east of the Mekong River (Nomascus concolor jingdongensis, N. c. concolor and N. c. lu); and another is found west of the Mekong River (N. c. furvogaster). In addition, there has been speculation that gibbons exist in the Biluo Snow Mountains, between the Mekong and Salween basins. To clarify the biogeography of this species, from April 2011 to January 2012 and from January 2016 to September 2018, we conducted interviews with local villagers, completed line transect surveys, monitored gibbon calls, and placed 30 camera traps in the forest canopy. On October 30, 2016, we recorded gibbon's calls. On July 5, 2016, our camera traps obtained one image of a male gibbon, and on February 1 and 8, 2017, we captured two independent images of an adult female gibbon on Zhiben Mountains. Based on the black crest on the head, clearly visible in the photographs, the gibbons are N. c. furvogaster. Evidence from interviews and survey records indicate that N. c. furvogaster once was present in the Zhiben Mountains, at an altitude of between 2000 and 2700 m. Between 1990 and 2000, some 6-7 groups still existed in Caojian, Laowo and adjacent areas. Unfortunately, in the absence of an effective conservation strategy, the population was extirpated by hunters. The remaining forest in the Zhiben Mountains is highly fragmented, and most of the suitable habitat for gibbons has been lost. Therefore, we expect that this newly found gibbon population is under extreme anthropogenic pressure. It is imperative that further investigations of this gibbon population be conducted immediately, and that the local and national governments implement effective conservation plans, including educating the local communities to protect this critically endangered primate population.