For women with a defined risk for breast cancer, five years of systemic hormonal therapy has been demonstrated to effectively reduce this risk. This therapeutic approach to breast cancer prevention is, however, limited by adverse effects that result in diminished patient compliance. In a previous study, we demonstrated that locally delivered fulvestrant using a silicone-based passive diffusion drug eluting implant could inhibit tumor growth in mice, while minimizing systemic exposure21. In this study, we sought to determine whether this approach could prevent breast cancer from developing while maintaining minimal off target exposure in a well-established rat breast cancer prevention model and in sheep using a localized delivery implant scaled for the breast.
In vitro characterization of fulvestrant eluting implants
Previous first-generation silicone-based fulvestrant eluting implants were scaled in size to accommodate mouse studies. These implants consisted of silastic silicone tubing, 1.6 to 2 cm in length, filled with powdered fulvestrant and sealed on both ends with silicone adhesive. Fulvestrant eluted from these implants by passive diffusion exhibiting zero order kinetics, with tubing wall thickness governing the release rate21. To assess larger implant and form factor designs to cover a larger area of breast tissue with ensured drug content uniformity, an alternate formulation of silicone and fulvestrant was created. To this end, fulvestrant was dissolved in ethanol and mixed into liquid silicone elastomer base (25 mg/g). Silicone tubing could then be filled with the silicone elastomer-fulvestrant mix by syringe and the elastomer mix allowed to cure forming a solid implant with an inner reservoir of fulvestrant-embedded silicone surrounded by the outer tubing layer.
To characterize the drug eluting potential of this design, cured silicone implants were cut to 4 cm in length (Fig. 1A). Solvent extraction demonstrated 4 cm length implant segments (N = 5) contained an average of 1096±100 µg fulvestrant (Fig. 1B). An in vitro elution study was conducted to characterize the release profile of fulvestrant. Implants (4 cm, N = 5) were placed in vials and allowed to elute into a solution of 1% SDS. Implants were serially transferred to new vials with 1% SDS at the indicated times to ensure the elution rate was not diminished by the fulvestrant already eluted and solubilized. Fulvestrant elution from these implants was evaluated for 194 days. The elution rate profile exhibited 2-phase kinetics (Fig. 1C), which were characterized by an initial burst of release (~ 31 µg/day after 24 hours) that rapidly decreased through day 11 (~ 9 µg/day), followed by a relatively slow decay to the end of the study (~ 3 µg/day). After collection of the final time point (day 194), remaining fulvestrant in each implant was extracted to determine percent depletion for each (Fig. 1D). The sum of total fulvestrant eluted and extracted was used to calculate total fulvestrant formulated in each implant. The calculated mass balance (1149±113 µg/implant) was comparable to fulvestrant amounts determined from manufactured implants of the same batch (1096±100 µg fulvestrant, Fig. 1B). Over the course of the study, the implants delivered 696±51 µg of fulvestrant or 61.8±1.6% of the total content (Fig. 1C).
Locally delivered fulvestrant delays breast cancer in the 7,12-dimethylbenz[a]anthracene treated female rat
7,12-dimethylbenz[a]anthracene (DMBA)-induced breast cancer in female Sprague-Dawley rats has been shown to closely recapitulate human estrogen receptor positive-hormonal therapy sensitive disease evolution. Following a single dose of DMBA, one or more tumors begin to arise within the mammary tissue typically between 100 and 200 days22. Systemic treatment with the anti-estrogen tamoxifen can prevent or inhibit growth of established tumors23. As such, this model was chosen to test the hypothesis that locally delivered fulvestrant from a drug eluting implant can be used to prevent or delay breast cancer.
Mature female Sprague-Dawley rats (N = 90) were randomly divided into three cohorts: For animals receiving either fulvestrant-loaded or sham implants, implants (4 cm in length) (N = 4) were surgically placed subcutaneously and adjacent to mammary tissue running cranial to caudal on both the left and right side of the animal (refer to Fig. 2A). Starting at the same time, animals in the systemic cohort received 12.5 mg/kg fulvestrant as a subcutaneous injection weekly until the end of the study. Two weeks following implantation surgeries, all animals were administered 20 mg of DMBA to initiate tumorigenesis. Of these, 10/90 animals died or required euthanasia within 7 days of DMBA administration. Remaining animals received either systemic fulvestrant treatment (N = 29), fulvestrant delivered locally via drug eluting implant (N = 28), or sham implants without fulvestrant (N = 23). The primary endpoints of this study were time to first tumor occurrence and overall survival. The study was concluded when all animals in the locally treated cohort reached a study endpoint (Table 1). Similar to previous reports, animals receiving systemic fulvestrant exhibited significantly prolonged time to first tumor (median 330 days) compared to locally treated (median 226 days, HR = 0.308, P < 0.0001) and animals receiving no drug (median 186 days, HR = 0.222, P < 0.0001). Only 6 of 29 animals receiving systemic fulvestrant developed mammary tissue-associated tumors by the conclusion of the study (Fig. 2B and D). Implant-delivered fulvestrant also significantly delayed time to first tumor compared to animals receiving no drug (median 226 versus median 186 days, HR = 0.510, P < 0.010). Systemic administration of fulvestrant, further, increased animal overall survival (median 367 days) compared to both locally treated (median 276 days, HR = 0.299, P < 0.0001) and animals receiving no drug (median 256 days, HR = 0.259, P < 0.0001). Although locally treated animals exhibited numerically longer overall survival, this did not reach statistical significance (HR = 0.763, P < 0.304) (Fig. 2C). For both locally and systemically treated animals, no benefit was observed in extended survival following development of the first tumor (Fig. 2D).
Table 1
Rat breast cancer prevention study cause of death
| | Treatment cohort (N, %) |
| | Systemic (N = 29) | Local (N = 27) | Untreated (N = 23) |
Cause of death |
Tumor burden | 1 (3.4) | 19 (70.4) | 19 (82.6) |
End of study | | | |
| non-tumor bearing | 12 (41.4) | - | - |
| tumor bearing | 1 (3.4) | - | - |
Ulcerated mass/skinA | | | |
| non-tumor bearing | 7 (24.1) | - | - |
| tumor bearing | 3 (10.3) | 3 (11.1) | 1 (4.3) |
Weight loss/BCSB | | | |
| non-tumor bearing | 4 (13.8) | 2 (7.4) | 3 (13.0) |
| tumor bearing | 1 (3.4) | 3 (11.1) | - |
Anon mammary tissue associated lesions | |
Bbody condition score < 2 | | | |
Findings from our study demonstrate that the anti-estrogen fulvestrant significantly delays tumor formation and potentially prevents breast cancer, as well as increasing survival when provided systemically in the Sprague-Dawley rat DMBA model which served as a positive control. Here, we show for the first time that fulvestrant when provided locally via a drug eluting implant can also delay tumor formation.
DMBA rat study fulvestrant tissue biodistribution
A key hypothetical benefit to local fulvestrant delivery as a means to prevent breast cancer is achieving efficacious target tissue drug levels, while substantially minimizing off target exposure. Plasma samples of rats in systemic and locally-delivered fulvestrant were collected on days 45, 72, 101, 130, 164, 172, and at time of necropsy for animals that exited the study. At the time of necropsy additional tissues were collected including mammary fat pads, kidneys, liver, and tumors. Additionally, all implants of the locally treated cohort were collected and the remaining fulvestrant in the implants was measured to calculate the cumulative release from the implant at the time of harvest.
When samples across all times are compared, animals receiving systemic treatment exhibited ~ 32-fold higher median fulvestrant plasma concentrations compared to local treatment (24.65 versus 0.76 ng/mL, P < 0.0001) (Fig. 3A). Over the course of the study (Fig. 3B), the median plasma fulvestrant concentration in the systemic cohort increased through day 164, and then plateaued through day 172. Tumor occurrence and animal euthanasia started after day 173, which resulted in a considerable increase in plasma level variance and a decrease in median plasma levels. Yet there was no clear correlation between end of treatment (EOT) fulvestrant plasma levels and the presence of tumors or tumor burden. For local treatment (Fig. 3C), median fulvestrant plasma remained low and stable through day 164, after which it significantly dropped. For this cohort, 20 of 28 animals developed the first tumor following day 164. However, compared to the systemic cohort, across all samples, tumor bearing animals had significantly less median plasma fulvestrant levels (0.38 ng/mL) than non-tumor bearing animals (0.83 ng/mL, P < 0.018, Fig. 3D). In addition, of the 18 animals in this cohort for which plasma samples were collected, 17 had fulvestrant plasma levels below 1 ng/mL at the time of tumor development, suggesting tumor occurrence results from decreased fulvestrant in a specific implant or a decrease in fulvestrant release over time.
The kidney and liver are the primary organs of fulvestrant metabolism and clearance and exhibit highest tissue concentrations across animal models and humans21. In animals systemically treated, both kidney (298.1 ng/g, Fig. 3E) and liver (132.4 ng/g, Fig. 3F) exhibited greater median fulvestrant concentrations than found in plasma (24.65 ng/mL, Fig. 3A). In stark contrast, minimal to no fulvestrant was detected in the kidney (median 0.15 ng/g) and liver (undetectable) of locally treated animals. Mammary fat pads were divided by quadrant and individually assessed for fulvestrant concentration. Consistent with other tissues, median fulvestrant concentration in the mammary fat pads of the systemic cohort was significantly higher than that in the local cohort (111.3 versus 8.5 ng/g, P < 0.0001, Fig. 3G). However, the local cohort exhibited more efficient on target delivery with a ratio of median mammary fat pad to end of treatment plasma ratio of 21.8 versus 5.4 (P < 0.0034) for the systemic cohort (Fig. 3H). All tumors evaluated in the local treatment cohort (0 to 72.6 ng/g range, N = 62) had a lower fulvestrant level than those in the systemic treatment cohort (211 to 85092 ng/g range, N = 4). Furthermore, 36 of the 62 tumors evaluated in the local cohort had undetectable fulvestrant (Fig. 3I) suggesting tumors arose due to limited fulvestrant delivery.
As hypothesized, local fulvestrant treatment resulted in significantly less systemic exposure. Furthermore, on target fulvestrant delivery was more efficient for local compared to systemic delivery. Tumors that arose in locally treated animals primarily occurred when fulvestrant delivery diminished, indicted by a significant drop in plasma levels over this span. Consistent with decreased delivery, these tumors were found to have minimal to no fulvestrant levels. In contrast, the few tumors that arose in systemically treated animals, which maintained relatively high plasma fulvestrant levels through end of treatment compared to locally treated animals, had substantially higher fulvestrant levels and thus likely developed resistance to fulvestrant.
Expected versus actual fulvestrant delivered via the drug eluting implants
End of treatment plasma samples from the locally treated animals were significantly diminished compared to earlier points in the study (Fig. 3C) and harvested tumors contained little to no detectable fulvestrant (Fig. 3G). This reduced delivery could be explained by a drop in the rate of release because of implant fulvestrant depletion, perturbation of release caused by fibrotic encapsulation of implants overtime, fulvestrant degradation, or potentially a combination of these. In vitro release rate characterization for 194 days (Fig. 1) did not result in the detection of novel fulvestrant degradation products or metabolites during HPLC quantitation that would suggest compound degradation over time (data not shown). From this idealized release experiment, designed to eliminate imperfect sink effects, a power fit of the release data (R2 = 0.985, Fig. 4A) predicts ~ 79% and ~ 89% of implant fulvestrant was delivered by day 300 and 385, respectively. To assess actual delivery, retained fulvestrant was extracted from implants recovered during end of study animal necropsy. Substantial variance in extracted fulvestrant across the four implants from the same animal was observed. Implants from most animals (18 of 23) averaged delivery of fulvestrant near or less than the predicted amount based on extrapolation of the in vitro curve fit. Values exceeding the predicted release may be due to formulation variations or incomplete fulvestrant extraction resulting from implant adherent tissue. At necropsy, implants were observed to be associated with remnant fat or connective tissue to varying degrees, which may have affected extraction efficiency.
To better understand the potential influence of fibrotic encapsulation on implant fulvestrant elution, a subcutaneous mouse model was employed to assess encapsulation over time24. To this end, CD-1 female mice were implanted subcutaneously with 3 mm long versions of the fulvestrant eluting implant used in the rat breast cancer prevention study. Implanted mice were divided into four cohorts (N = 5 per cohort). Implants with surrounding tissue were harvested from one cohort after 2, 4, 8, and 16 weeks, respectively. The tissue was formalin fixed and paraffin embedded. Sections were trichrome stained to visualize fibrotic tissue and implant surrounding capsule thickness was measured (Fig. 4B and C). For individual implants, capsule development remained relatively consistent (ranging from 19.8±11.3 to 24.5±22.0 µm), punctuated by small regions of increased thickness. This was observed in the earliest cohort (week 2), however, no significant difference in capsule thickness was observed in subsequent cohorts through 16 weeks.
Taken together, these results suggest that implants delivered fulvestrant in vivo close to that predicted by the in vitro elution study. Less than predicted delivery was likely a combination of imperfect sink conditions surrounding implants and fibrotic encapsulation. However, the drop in plasma observed at later time points was more likely due to diminished fulvestrant implant reserves rather than decreased release from increasing encapsulation.
Safety and tissue distribution of locally delivered fulvestrant in Suffolk Cross ewes
Critical to efficacy of a drug eluting implant placed in the target tissue is sufficient distribution of the therapeutic throughout the mammary tissue. Ovine mammary tissue exhibits comparable histological features and volume to the human breast and25,26, as such, ewes have been used in a variety of procedure-based studies requiring a breast model27–29. To evaluate safety, target tissue distribution, and systemic exposure of fulvestrant delivered via a drug eluting implant, a Suffolk Cross ovine model was employed. Implants consisted of ~ 50 cm of silicone tubing filled with 2.5% fulvestrant cured in elastomeric silicone (w/w). The tubing was arranged in a spiral pattern and cured to a disc of silastic silicone (6 cm diameter, 0.3 cm thick) (Fig. 5A). In two ewes, this implant prototype was surgically placed within the udder and flat against the abdominal wall with the tubing face anteriorly directed into the glandular tissue. After 30 days, the animals were euthanized and underwent necropsy. Plasma, liver, kidney, and the implant containing udder were harvested for subsequent analysis. No gross abnormalities were observed by the study veterinarian.
Following implant removal, the harvested udder tissue was evaluated for histopathology. The implant lumens were found to be surrounded by a fibrous capsule (2.11±0.81 mm, Fig. 5B), which multifocally extended into the interlobular tissue. Within the capsule, clusters of lymphocytes, neutrophils, and, to a lesser extent, plasma cells were observed. Further, pockets of macrophage and occasional giant cell infiltrate were found in the adipose tissue of the gland proximal to the implant. Beyond histological changes associated with mild fibrotic encapsulation, no microscopic lesions were found within the glandular tissue.
Systemic exposure resulting from locally delivered fulvestrant was assessed by quantifying drug in plasma and known tissue reservoirs, namely the kidney and liver, organs of metabolism and clearance (Table 2). Plasma levels were 1.2±0.5 ng/mL, with a ~ 3-fold but low accumulation in liver and kidney tissue (3.3±0.08 and 3.8±0.81 ng/g, respectively). To assess fulvestrant distribution through the udder, 5 mm punch biopsies were taken from the capsule, muscle/fascia between the capsule and abdominal wall, glandular tissue within 0–5, 5–15, and > 15 mm from the capsule, and the glandular cistern (Fig. 5C). Highest fulvestrant values were found in the tubing-facing capsule (234.5±150.6 ng/g) and glandular tissue adjacent to the capsule (142.3±68.9 ng/g). Fulvestrant levels decreased with distance from the capsule. Fulvestrant levels were also detected in the glandular cistern (15.5±1.0 ng/g) and tissues between the dorsal facing capsule and abdominal wall (18.1±2.0 ng/g), however, as anticipated from the increased thickness of the backwall of the implant, these levels were lower.
Table 2
Sheep fulvestrant tissue biodistribution
| | | Fulvestrant, ng/g |
Tissue | Mean | SD |
PlasmaA | 1.2 | 0.5 |
Liver | | 3.3 | 0.8 |
Kidney | 3.8 | 1.0 |
Udder | | |
| Capsule | | |
| | Dorsal facing | 76.9 | 27.0 |
| | Ventral facing | 234.5 | 150.6 |
| GlandularB | | |
| | 0–5 mm | 142.3 | 68.9 |
| | 5–15 mm | 30.5 | 9.2 |
| | > 15 mm | 18.3 | 5.5 |
| Muscle | 18.1 | 2.0 |
| Glandular cistern | 15.5 | 1.0 |
Ang/mL | | |
BDistance from the capsule | |
In summary, this 30-day sheep study demonstrated indwelling fulvestrant eluting implants were safe and elicited no local toxicity. Implants did provoke a foreign body reaction with moderate inflammation that did not prevent fulvestrant elution. Eluted fulvestrant penetrated through the fibrotic capsule and deep into the surrounding glandular tissue. In contrast, systemic exposure was low with plasma levels significantly lower than target tissue levels.