Study on the linear absent section ratio (L-ASR) of earthen sites and anthropogenic influence from the perspective of population density

Having extremely high artistic, scientific and social values, earthen sites are widely distributed in China and are important human cultural relic resources. Due to accumulated natural erosions (from rain and wind) and human activities (destructive activities of human beings in history and modern times), however, earthen sites have been greatly damaged, and many sections have even been absent, so that they are seriously threatened by extinction. Under these circumstances, acquiring the conservation status of earthen sites is a vital prerequisite for the subsequent targeted protection. In this paper, as a world-renowned heritage site, the castles of the Ming Great Wall located in Qinghai Province were selected as the research object. A novel indicator, namely the linear absent section ratio (L-ASR), was proposed, and its value was classified into five levels to quantitatively characterize the specific conservation status of such sites, including excellent (E) (0–10%), good (G) (10–25%), fair (F) (25–50%), poor (P) (50–75%), and very poor (VP) (75–100%). Based on the assessment results, the castles with excellent status constituted the minimum proportion, while the castles with very poor status represented the largest percentage, reflecting the grave situation of earthen sites. Furthermore, by applying population distribution models to the linear fitting combined with the population density (PD), a positive correlation between PD and L-ASR was obtained to reveal the anthropogenic influence on the destruction of earthen sites. Principal component analysis (PCA) was utilized to provide a far richer understanding of which factors correlate most strongly with deterioration. This study provides a new thought to quantitatively characterize the preservation conditions of earthen sites and also indicates the effect of human activities on the damage of earthen sites from a population density perspective, which is potentially used for the analysis of more various types of architecture with different construction techniques. Hence, this approach is beneficial to the overall damage assessment of earthen sites, and also meaningful to their further preservation and protective planning.


Introduction
Earthen sites are typical architectural sites mainly built with soil materials, and they are widely distributed throughout the world in places such as Ajina Tepa, long historical process stretching from the Paleolithic Age to modern times, reflecting the evolution of Chinese civilization and the improvement of social productivity [10,11]. There are many earthen sites located in NW China, and the climatic location of these sites has harsh weather characteristics, including drought, low rainfall, high winds and strong evaporation. Undoubtedly, they are important human cultural relic resources. Because of exposure to long-term natural forces, including wind and rain erosions and human activities, these earthen sites have developed many deteriorations, such as sapping, cracks, scaling off, gullies, collapses, etc., severely threatening their preservation [5,[12][13][14][15]. Under the current circumstances, most earthen sites have been seriously damaged, and many sections have even been absent due to the development of deteriorations and natural/human influences over thousands of years, so their existence is greatly threatened. Consequently, the targeted protection of earthen sites is very urgent, and securing the conservation status of these earthen sites starting from these absent sections is a vital prerequisite for the protection work.
To date, many scholars have mainly focused on the mechanisms of deterioration at earthen sites, as listed in Table 1: Four deterioration categories, including property deterioration, structure damaging, structure collapse, and site destroying, have been identified [13]; On the basis of field investigation and laboratory analysis, four main deterioration modes, namely wind-related deterioration, water-related deterioration, temperaturerelated deterioration and chemical-related deterioration were identified at the Jiaohe ruins in China [15]; A model characterizing the deterioration at the earthen sites of the Ming Great Wall in Qinghai Province was also proposed to reveal the mechanisms and evolution of deterioration from a macro perspective [5]. Based on these deterioration developments, the damage assessment of earthen sites was studied by means of multicriteria decision-making (MDCM) and machine learning methods combined with environmental factors and building material indices, which revealed the local damage to earthen sites caused by the development of deteriorations [12,16]. However, a scientific approach to assess the overall damage of earthen sites and quantitatively illustrate their conservation status is still lacking. The effects of natural factors on earthen sites, such as wind, rain, earthquakes, etc., have mostly been studied [14,17,18], but few studies have focused on the quantitative influence of human activities.
In fact, human activities have very significant effects on the damage of earthen sites, and even artificial destruction in historical and contemporary processes has been regarded as a deterioration type [11,13,15]. For instance, local farmers directly dug soils at earthen sites (Fig. 1a), randomly add buildings along with earthen sites (Fig. 1b), and even dwell behind earthen sites so that the earthen wall is used as a home enclosure ( Fig. 1c and d). Some farming activities (Fig. 1e) and road engineering (Fig. 1f ) activities have also influenced earthen sites conservation. However, to implement the Rules on the Great Wall Protection, the overall protective planning of the Ming Great Wall in Qinghai Province has been conducted in an orderly manner, which has effectively restricted human destruction under the joint governmental and individual efforts [19]. To protect the Ming Great Wall in Qinghai Province, conservation management and protection systems have been established and improved. Specifically, the local protection departments have set up logs and files for the Great Wall sections for which they are responsible, the government has strengthened related law enforcement, scholars are using advanced technology and materials to consolidate damaged earthen sites, and regulators have combined the technical monitoring and manual monitoring approaches to prevent human activities. Such work has effectively slowed down the destruction process of the Ming Great Wall. According to the research about the correlation between human activity intensity and population density by counties in China in 2008, there exists a positive exponential function with a high correlation coefficient (R = 0.8156) [20]. This means that the population density can be regarded as an effective Table 1 The research status of the mechanisms of deterioration of earthen sites indicator to show the degree of human activity, so it is a good metric to be used for assessing anthropogenic impact. Therefore, this research aims to investigate the anthropogenic influence on earthen sites from the perspective of population density.
In this paper, the authors selected 46 castles of the Ming Great Wall located in Qinghai Province, China, as the research object and proposed a novel indicator, namely the linear absent section ratio (L-ASR), to characterize the conservation of such sites. Moreover, as human destruction has been regarded as one of the typical deterioration types of earthen sites [13,15], the authors decided to focus on the impact of humans as a correlation to earthen site damage in order to prove and determine their influence on earthen site damage. The anthropogenic influence on the L-ASR was researched from the perspective of population density (PD). By applying population distribution models, PD was further correlated with L-ASR to show the effect of human activities on the damage of earthen sites from a macroscopic perspective. The research results show the potential to promote the indicator and model proposed in this study into earthen sites and even many types of architecture built with any type of construction technique, because the materials and techniques of buildings were not considered in the assessment process proposed in this research. The research findings provide beneficial references to the overall damage assessment of earthen sites and are also meaningful to their further preservation and protective planning.

Study sites
The Great Wall built during the Ming Dynasty, called the Ming Great Wall, was the most renowned military defensive project in ancient China and was designated as a World Heritage in 1987 [21]. The Ming Great Wall is a complex military network consisting of walls, trenches, beacon towers, passes, castles, precipitous mountain areas, marine insurance, etc., and these building types played their respective roles and were coordinated for military defense [22]. In the whole Great Wall system, the castle was a core element with multiple functions, including the exchange of military information, goods and people, and the management of important civil affairs [23,24].
Located independently from the Great Wall mainline in "nine towns", the Ming Great Wall in Qinghai Province is a significant section of the whole Great Wall, which was built from 1546 to 1596, surrounding Xining Wei with an arch shape [22,25]. Due to the rammed earth being vulnerable to climate erosion, the Ming Great Wall has severely deteriorated as a form of earthen sites [16,26]. As a significant part of the Ming Great Wall, 46 castles are located in Qinghai Province (Fig. 2), which were selected as the study object to research their conservation status. These castles coincide with the selection of case studies in a previous study on their architectural features and military functions [24], which is a significant extension and justification of our previous research. Information on these sites is listed in Table 2. As for the distribution of the 46 castles, some castles were located near the main wall, while some were located far away

Methods
The Great Wall is one of the most representative lineal cultural heritage sites in China and has a linear distribution pattern across 15 Chinese provinces with a total length of 8851.8 km [27,28]. To date, a large number of wall sections have been absent over the course of hundreds of years. It is important to measure the absent length of the wall when evaluating the conservation status of the Great Wall. In this research, the linear circumference indicates the whole length of the perimeter of the castles including their north, east, south and west walls, called circumference length (CL), and the length of remaining wall sections is called the remaining length (RL). Linear circumference data were collected from archaeological materials, including survey reports on the Ming Great Wall in Qinghai Province and castle plane graphs provided by the Qinghai Provincial Administration of Cultural Relics and the Qinghai Bureau of Surveying and Mapping, which organized comprehensive investigations on the Great Wall from 2007 to 2009. The wall length of castles can be extracted and measured from these materials.
By collecting archaeological materials from these such sites, the CL and RL of the walls can be acquired. According to the survey reports on the Ming Great Wall in Qinghai Province provided by the Qinghai Provincial Administration of Cultural Relics and the Qinghai Bureau of Surveying and Mapping, the length of remaining and absent wall sections can be collected. To correct this length data, the castle plane graphs provided by the Qinghai Provincial Administration of Cultural Relics and the Qinghai Bureau of Surveying and Mapping were imported in Auto CAD to measure the absent wall sections. The plane graphs were drawn by the archaeological investigation team using orientations and plotting scales to reflect the site plane layout.
The authors proposed a novel indicator called the linear absent section ratio (L-ASR), which is mainly applied to quantitatively characterize the ratio of the absent wall's linear length to the circumference length of the castles by measuring the CL and RL to reflect the overall damage or material damage of the lineal cultural heritage since they were built up, according to the following calculation: where RL/CL is the remaining length ratio (RLR). The castle CL and RL data can be acquired from the  [24] measurement of plane graphs in Auto CAD. The proposed assessment methods are applicable to pre-existing architecture with other types of materiality because the index of L-ASR reflects the percentage of material mass that the element has lost, based on a comparison of surfaces measured in plane graphs.
The value of L-ASR can be classified into 5 levels to quantitatively characterize the specific conservation status of the castles, including excellent (E) (0-10%), good (G) (10-25%), fair (F) (25-50%), poor (P) (50-75%), and very poor (VP) (75-100%). Because there has not been a uniform method of damage division for earthen sites thus far, in this research, the authors mainly referred to the classification approach used for the rock quality designation (RQD), which is still the only rock mass classification index available. RQD is an index of rock quality in which a modified core recovery percentage is obtained by counting only pieces of sound core 10 cm or greater in the length of NX size or large core diameters, which is an important indicator of rock quality classification [29].
After that, the authors introduced the index of population density (PD) into this research. The PD indicates the number of people living in each unit of area (such as a square kilometer), which is an important indicator for measuring the distribution of population in a region [30]. Its formula was shown in Eq. (2): where PN is the number of population in a certain region, and RA is the area of that region. The population number of each village was collected from the survey results on the Ming Great Wall in Qinghai Province provided by the Qinghai Provincial Administration of Cultural Relics and the Qinghai Bureau of Surveying and Mapping, which organized comprehensive investigations on the Great Wall from 2007 to 2009. From that investigation activity, the population number in villages where castles were located in or nearby can be found in 2008. The population region of each village can be found and measured using Rivermap X3 software. By using the measuring tools in this software, the area of the population region can be determined.
Using the above procedures and methods, the L-ASR values of 46 castles can be acquired. The data of RL and CL can be collected, and then L-ASR data can be calculated based on Eq. (1), and the conservation status can be determined according to the L-ASR values and classification levels.
Finally, four frequently used single core population distribution models were applied to achieve positive correlations between PD and L-ASR, showing the influence of human activities on the conservation of earthen sites from a macroscopic perspective. Because the population number in this research is only collected from the archaeological materials in 2008 provided by the Qinghai Bureau of Cultural Heritage, and the L-ASR data can also reflect the destruction status of castles in 2008, as the overall survey of castles was carried out in that year, a good corresponding relationship between PD and L-ASR was determined in this paper. Some castles are located in villages, while others are located out of the villages at a certain distance. The distance should be a nonnegligible factor for the damage caused by human activities. The reason why four different core population models were used is that the distance between castles and villages can be considered as an important factor in the quantitative study of the anthropologic influence on earthen site destruction. Furthermore, it should be beneficial for the heritage management to use four different core population models, providing a helpful theoretical basis for protection measures for earthen sites at a certain distance from the place where people gather, such as the addition of the fence and monitoring systems. Specifically, by collecting the population number and region area of the village, a conservationist can calculate the theoretical damage degree of an earthen site located outside or inside of a village with the help of the single core population distribution model to determine the level of preventative effort, and definitely, the data of distance between the site and village are necessary to process this calculation.

Linear absent section ratio (L-ASR)
The authors first calculated the L-ASR value of the No.1 of Chengbeihou Castle by measuring its size on the plane graph in Auto CAD. As shown in Fig. 3 Table 3.
In Table 3, the conservation status of each castle can be acquired based on the L-ASR values and corresponding classification ranges: there are no castles with an excellent status; 10 castles have a good status, making up 22% of the total castles; 9 castles have a fair status, accounting for 20%; 10 castles (22%) have a poor status, and 16 castles (36%) have a very poor status (Fig. 4). Hence, castles with excellent status constituted the minimum proportion, while castles with very poor status represented the largest percentage. More than half of the castles are in poor condition or worse. These grading evaluation results reflect the grave situation of the earthen sites. Furthermore, the authors compared the conservation status of castles in G, F, P, and VP levels determined by the L-ASR index with their actual situation by choosing four representative castles (No. 18, 20, 40 and 45 castles), which can be seen in Fig. 4. According to this comparison, the castles were damaged more seriously as the damage level calculated by the indicator of L-ASR increased.
These research methods and results could provide helpful and effective suggestions for the conservation status of the 46 castles because the L-ASR is a very useful indicator to reflect the overall damage or material   [24,25]. Combined with the L-ASR results, the relationship between the military functions and conservation status of castles in Qinghai Province can be obtained in Fig. 5. In general, when prioritizing castle conservation at the same level of conservation status based on L-ASR results, the value of castles should be taken into account so that a comprehensive consideration can be made, including the value levels and L-ASR results: the Wei castle should be given the highest values, as it is at the highest military level (the political, economic, and military center of M-GWMDS), Suo castles should have the secondary value level, and Bao castles should have the lowest level. In terms of the castle for garrison, the garrison city has a higher military level than the garrison castles based on the size of the architecture and the garrison, so it should have more values and higher priority ratings than the garrison castles.

Population density (PD)
In this study, most castles are located in or near a certain village. The authors collected the number of residential populations in these villages from archaeological materials provided by the Qinghai Bureau of Cultural Heritage, and measured the living area of such villages via Rivermap X3 The circumference length data of No. 43 castle cannot be obtained because it has been damaged very severely and from historical documents, there were no related records about its size

Fig. 4 The conservation status of castles in Qinghai Province
software. Then the PD of the villages could be further calculated. The related data were listed in Table 4. Combined with castle conservation status results previously acquired, the authors averaged all PD data of villages where the castles in each same damage level are located. As shown in the box plot (Fig. 6), with the increment of overall damage level, the average PD data steadily increased from 4860 per km 2 in the G status to 8679 per km 2 in the VP status. This means that the conservation status of earthen sites would worsen as the surrounding population grows from the perspective of data averaging.

The correlation between PD and L-ASR
After acquiring the PD data of villages and L-ASR of castles of the Ming Great Wall in Qinghai Province, the correlation between PD and L-ASR was studied to further reveal the anthropogenic influence on the conservation of earthen sites. In fact, many castles in this research are not located in villages but near those villages, so the population density attenuation along with the distance between castles and villages should be considered. Four frequently used single core population distribution models were applied, including the Clark, Smeed, Newling, and Cubic models [31][32][33][34], to calculate the population density of castles with the attenuation of the PD of villages that have a certain distance from castles.
The Clark model uses a negative exponential function to indicate the relationship between PD and distance from the residence center, as shown in Eq. where PD r is the population density of a place with a distance of r from the residence center, PD 0 is the population density of the residence center, and b, c and d are parameters. In this study, if a castle was located in a village, then its distance was regarded as 0 m; if it was located outside of a village, then its distance was measured between the centers of the castle and the nearest village. The population distribution is assumed to be the single core, meaning that a single village's influence on castle damage was only considered. Furthermore, the PD r is the assumed population density of castles with the attenuation of the PD of villages, PD 0 is the population density of villages, and r is the distance between the castle and village.
Combined with related archaeological materials and Rivermap X3 software, we collected and measured the data of distances between castles and villages in which they were located or nearby, as listed in Table 4. After that, it is assumed that there is a linear positive correlation between PD r and L-ASR. During processing the related data, the PD 0 and L-ASR of castles that have the same distance from villages where they are located were calculated as the average value. Eventually, there were 17 groups of data to conduct the fitting, which are shown in Table 5.
To achieve optimal fitting effects, the Levenberg-Marquardt (LM) optimization algorithm was used to determine the parameters in Eqs. (3)(4)(5)(6). After that, PD r can be calculated and the correlation between PD r and L-ASR can be further determined, as shown in Fig. 7. From the correlation results, the Cubic model has the largest correlation coefficient (R = 0.6415), compared to the other three models. Therefore, the positive correlation between PD and L-ASR can be proved, and the anthropogenic influence on the conservation of earthen sites was revealed from a macroscopic perspective. The 3D data (DEM) were applied to illustrate the conservation status of earthen sites, as shown in Fig. 8. The Cubic model has been used to show the anthropogenic influence from the PD perspective on the destruction of earthen sites by taking No. 1 and No. 2 castles as an (4) PD r = PD 0 r b (5) PD r = PD 0 e br + cr 2 (6) PD r = PD 0 e br + cr 2 + dr 3 example. Figure 8 shows the spatial distribution of the conservation status of castles and the PD distribution obtained by applying the Cubic model to the Chengbeihou Village, and its nearby castles, i.e., the No. 1 and No. 2 castles. It is true that if more than one village was close to one certain castle, they would contribute to its damage. We surveyed all castles in this study and found that 24 castles were located in villages, 19 castles were located near villages within 1 km, and the others were far away from villages. For the castles near villages, we found that there was only 1 village in the distance range (1 km) of a certain castle, and villages with a distance greater than 1 km were not considered in the population distribution modeling. The reason is that the single core population distribution model can be a convenient and efficient tool to calculate the population density of castles with the attenuation of the PD of villages that have a certain distance from castles. If we consider villages more than 1 km from castles, the multicore population distribution model should be further researched and applied, which is a complex issue because more village population data are needed to process the fitting. However, population data in such far side villages are lacking. In fact, the population data were collected from the comprehensive investigations on the Great Wall from 2007 to 2009 organized by the Qinghai Provincial Administration of Cultural Relics and the Qinghai Bureau of Surveying and Mapping, and the team only collected the population data of the nearest villages from the castles. Therefore, it is difficult to consider the multicore population distribution model to study more villages contributing to the damage of castles. We acknowledge that there is a distance limitation in that our study only considered the influence of the nearest village on castle damage in the distance range of 1 km. In our future study, we will try to collect and expand more population data of villages in the application of the multicore population distribution model.  In this research, there are benefits and limitations for the L-ASR indicator. One advantage is simplicity, because it can be briefly calculated from only two parameters, namely castle circumference length (CL) and remaining length (RL), to reflect the overall damage condition of earthen sites. Another advantage is the application of satellite imagery. The data of the living area of the village and the distance between castles and villages were collected from the satellite imagery via Rivermap X3 software. In our future research, the use of satellite imagery in earthen site conservation will be further explored. However, there is a limitation for the L-ASR indicator, which cannot reflect the conservation state of the remaining wall, i.e., there is no distinction if the remaining wall is in good/poor condition. In fact, this issue has been addressed in previous research. The vulnerability assessment has been studied by applying AHP-TOPSIS to determine the damage assessment levels for the remaining wall from 18 earthen sites in Qinghai Province, combined with their occurrence environment, engineering properties of rammed earth, deterioration characteristics, and building technologies [12]. Therefore, this research is actually a good supplement for the study on the damage assessment of earthen sites, as it has worked out the proportion of absent walls in the entirety of earthen sites, which was not given in that previous research. Another limitation is that we cannot obtain the related data to reflect the chronological moments of destruction of the properties in relation to their population. The population and architectural length data were The aforementioned four population distribution models have a common assumption with the single core population distribution, meaning that the population density would generally decrease with the increment of distance from the residential center. According to the average value of L-ASR for castles located in villages and castles outside of villages, we obtained that the average L-ASR for castles in villages is 58.95%, which is higher than the average L-ASR (54.27%) for castles outside villages. Based on the Cubic model in Eq. 6, the population density generally decreases with increasing distance from the residential center. Such results can jointly explain why heritage assets located in towns are more at risk of deterioration than those located in uninhabited environments. Therefore, if the castle is much closer to the village, its conservation could be more obviously affected by more intense human activities, which has been proved from the fitting correlation results in Fig. 7. The flaw is that the correlation coefficient is not very large. The reason is that the population number has fluctuated with time. In particular, the Ming Great Wall has been built for approximately 500 years but the residential number in their locations each year is difficult to acquire. However, a good corresponding relationship between PD and L-ASR was studied in this paper because they were both survey data organized in 2008; in addition to human influence, the damage to earthen sites is also closely related to the erosion of wind and rain and the vulnerability of rammed earth materials [12,16]. To provide a far richer understanding of which factors correlate most strongly with deterioration, principal component analysis (PCA) was initialized using Minitab, including the population density calculated by the Cubic model, past climate data, and times of earthquakes per decade. The past climate data for the counties where 46 castles were located were collected from the Qinghai Meteorological Bureau, including annual rainfall and annual wind speed from 1961 to 2013, and the times of earthquakes per decade (2011-2021) were collected from the Data Sharing Infrastructure of National Earthquake Data Center [35], as listed in Table 6. The PCA results are shown in Table 7. The first three principal components accounted for 94.2% of the total variance, and rain and wind were the most relevant variables in the first principal component, while  A positive tendency between PD and L-ASR can be apparently seen from our research results, and the correlation coefficients passed the significance test and were statistically significant. Therefore, the indicator and model proposed in this research have scientificity and accuracy. In our future research, the L-ASR and PD models will be further promoted and applied to other sections of the Ming Great Wall in NW China to acquire more scientific and precise assessment outcomes of the conservation status of earthen sites by constantly revising and improving related parameters. Moreover, the volume reflection data including the remaining height and the top and bottom widths of earthen sites, will be collected, and then the volume absent section ratio (V-ASR) can be further studied in the future.

Conclusion
In this paper, 46 castles of the Ming Great Wall in Qinghai Province were chosen as research objects. The linear absent section ratio (L-ASR) was proposed to characterize the conservation status of earthen sites, which can be divided into five levels: excellent (E) (0-10%), good (G) (10-25%), fair (F) (25-50%), poor (P) (50-75%), and very poor (VP) (75-100%). By means of plane graphs of these castles, the remaining length (RL) and circumference length (CL) of castles were collected, and then L-ASR data were acquired.
Based on L-ASR values and corresponding classification ranges, there are no castles (0%) at the E status, 10 castles at the G status making up 22% of the total castles, 9 castles at the F status accounting for 20%, 10 castles (22%) at the P status, and 16 castles (36%) at the VP status, respectively. Hence, castles with excellent status constituted the minimum proportion (0%), while castles with very poor status represented the largest percentage (36%). More than half of the castles (58%) were in poor condition or even worse. These grading evaluation results reflect the grave situation of earthen sites.
Moreover, the population density (PD) of villages in which castles are located or nearby was obtained. Combined with the conservation status results of castles, the average PD data increased with the increment of overall damage level, meaning that the conservation status of earthen sites would worsen as the surrounding population grows from the perspective of data averaging.
By referring to four frequently used single core population distribution models, namely Clark, Smeed, Newling, and Cubic models, a linear positive correlation between the population density of a position where the castle is located (PD r ) and L-ASR was determined, and the Cubic model had the best fitting result. The population distribution model was the carrier to introduce an important factor in the quantitative study of the anthropologic influence on earthen site destruction, namely the distance between sites and villages. Furthermore, this is helpful for the heritage management by calculating the theoretical damage degree of an earthen site located outside or inside of a village. There are also main limitations in this research: the multicore population distribution model was not considered, and the chronological moments of destruction of the properties in relation to their population were not reflected due to the restrictions on receiving archaeological materials.
According to our research findings, the novel indicator, i.e., the L-ASR, can quantitatively characterize the ratio of an absent wall's linear length to the circumference length of castles by measuring the length of circumference length and remaining length, which is a very useful indicator to reflect the overall damage or material damage of the lineal cultural heritages since they were built up, and the anthropogenic influence on the damage of earthen sites has been revealed from a macroscopic perspective. This has the potential to further incorporate the indicator and model proposed in this research for the analysis of more various types of architecture with different materials or construction techniques, not only limited earthen sites, because the materials and techniques of buildings were not considered in the assessment process proposed in this research. As the L-ASR index only considered the length of the plane of castles, while the height and volume of the wall were not taken into account, the volumetric erosion of materials cannot be reflected at this moment. However, in our future research, the volume reflection data, including the remaining height and the top and bottom width of earthen sites will be collected, and then the volume absent section ratio (V-ASR) will be further studied. Therefore, this research is beneficial to the overall conservation assessment of earthen sites, and also meaningful to their further preservation and protective planning.